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Latest
Information regarding TCE contamination at Gates/Cherokee Sites
| UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
REGION 8
999 18TH STREET - SUITE 300
DENVER, CO 80202-2466
Phone 800-227-8917
Ref: 8EPR-ER June 6, 2005
Mr. Tom Reeves
Director, Corporate Development
Gates Corporation
1551 Wewatta Street
Denver, CO 80202
Re: TCE Contamination - Gates Property and Logan Street North of
Interstate 25
Dear Mr. Reeves:
This letter is provided to inform you that after extensive
investigation and reviewing information from the Voluntary
Cleanup Plan application of March 2, 2005, which the Gates
Corporation submitted, the U.S. EPA has concluded the Gates
property (Unit 47) trichloroethene (TCE) contamination is the
source of the plume migrating north along the east and west side
of Logan Street in Denver. The following summarizes the facts
that provide the basis for this conclusion:
1. Based on water level measurements from approximately 40 wells
in the area, it was determined that the direction of flow in the
deeper unit of the ground water is generally to the
north/northeast. A small, localized variation to that exists in
the vicinity of the Logan Street bridge at I 25, where the flow
is shifted to the southeast, apparently a function of the
de-watering system installed as part of the Interstate. These
data include measurements from EPA, IRG/Cherokee and ERM
installed wells.
2. Wells located along Mississippi Avenue, which are up gradient
from the Gates property are not contaminated with TCE either in
the shallow or deep groundwater units.
3. The enclosed map shows TCE is present in EPA wells ML-GP-18D,
35D, 13D and 8D all of which are down gradient of the Unit 47
area source. There is no other up gradient or direct source
identified in that area other than the source at Unit 47. The
presence of TCE only in the deep groundwater unit and not the
shallow unit is additional evidence that there are no TCE
sources in this area.
4. The deeper aquifer (or ground water unit) on the Gates
property is contaminated with TCE, specifically monitoring wells
MW7 and PZ1 are cases in point. Based on field screening and the
presence of solvent odor within soil samples, both these wells
are contaminated with chlorinated solvents within and below the
clay unit that separates the shallow and deep groundwater units.
Both wells are partially screened in the deeper groundwater
below the clay; MW7 has the highest trichlorethene (TCE)
concentration (52,000 micrograms per liter (g/L)) of all the
monitoring wells on the Gates property. The deeper groundwater
on the Gates property is hydraulically upgradient of the
residential area to the north/northeast and is an identified
source of the TCE contamination present in the deep wells in
this area.
5. Consideration was given to the presence of 1,1,1-
trichloroethane (TCA) in the plume located on the Gates property
and the general absence of TCA in the plume north of I-25. The
absence of TCA in association with the TCE in the deeper
groundwater plume to the north/northeast does not preclude the
Gates Property from being the source of this contamination for
the following reasons:
a. The ratio of TCE:TCA in the groundwater plume on the Gates
Property is at least 60:1 and generally greater than 100:1. TCA
would likely be non-detect in the deeper EPA wells to the
north/northeast. For example, MW-02 on the Gates property showed
TCE at 1175 ug/L with TCA not detected. Similarly, based on a
maximum TCE concentration of approximately 500 g/L to the
north, in wells installed by EPA, it is not likely that TCA will
be detected because the TCE:TCA ratio can be expected to
increase.
b. TCA is more strongly adsorbed to aquifer sediments(organic
carbon-water distribution coefficient (Koc) 281L/kilogram (L/kg)
than TCE (Koc 18 L/kg). As a result, the relative concentration
of TCE will likely increase compared to TCA as the plumes travel
downgradient. The TCE:TCA ratio will not be conserved but likely
increase with distance from the Gates Property. This further
reduces the likelihood of detecting TCA in the deeper EPA wells
to the north.
6. Although the shallow groundwater flow near I-25 and the Logan
Street bridge appears to be impacted by the highway, the
predominant flow direction and gradient in the deeper
groundwater unit are quite consistent, and there is no apparent
barrier obstructing deep groundwater flow under the highway.
Furthermore, historical contamination on the Gates property
preceded the construction of structures associated with the
highway and storm water drainage.
In conclusion, this information summarizes findings that will be
presented in a final report. Additional investigations may be
warranted to determine the extent of the ground water
contamination in that area and to evaluate the potential for
vapor intrusion into homes from ground water contamination. If
you have questions regarding these findings, please feel free to
contact me to arrange a meeting.
Sincerely,
Steven Way, OSC
Emergency Response Program
Enclosure
cc: Martin O’Grady, CDPHE
Janet Burgesser, DEH
Peggy Linn, EPA-OCPI
Chuck Figur, 8ENF-L
Felicia Hilton, City Council (w/ encl) |
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EPA Testing
of Groundwater And Initial Results
Near 1-25 and Logan Street
Denver, Colorado
Volume I, Issue I
January 2005
What Is EPA Doing?
The U.S. Environmental Protection Agency (EPA)
began an environmental investigation in the area around
Interstate 25 and Logan Street in Denver in the Fall of 2004.
The primary purpose of the investigation is to determine if
there is groundwater contamination under residential or
commercial buildings and if it might pose any potential health
risk to nearby residents. The contaminant of most interest is
trichloroethylene (TCE), used mainly as a solvent to remove
grease from metal parts. TCE can move from groundwater through
soil and as a vapor, enter buildings, usually through cracks or
openings in the foundation slab or a crawl space.
What Did EPA Find?
Initially, EPA sampled groundwater at locations
along Mississippi at Lincoln, Sherman, and Grants Streets. TCE
was not detected at these locations. In addition, EPA obtained
information from the Colorado Department of Transportation (CD
01) regarding the location of de-watering wells in which ICE was
detected during I-Rex construction. The wells were located east
of Buchtel Street in what is now the lightrail corridor along
1-25.
Consequently, EPA did more groundwater sampling in that area.
Sampling from 15 of 16 locations did not detect ICE. Sampling
from one location (north of 1-25 and on the east side of Logan
Street) detected ICE at a level of 910 micrograms per liter,
which is above the established federal and State of Colorado
drinking water standard of 5. EPA sampled again in this location
at a more shallow depth and found no ICE contamination.
What Will EPA Do Next?
EPA will do additional sampling. We will sample
at deeper depths at the location where the TCE was detected, and
we will sample existing wells located on the U.S. Postal Service
facility at Logan and Kentucky Streets.
All well locations and elevations will be surveyed to determine
the direction of the groundwater flow. This information is
needed to better under-stand the movement of the groundwater and
will help us to track any contamination. Groundwater flow in
this area is complicated. The retaining wall put in by CDOT, as
part of its T-Rex construction, further complicates flow.
If we find contaminated groundwater at shallow depths under
residential areas, we will conduct sampling in the home, as
appropriate, to deter-mine if there are vapors directly
underneath the foundation and if indoor air sampling is
warranted.
Give Us A Call!
Steve Way
Diane Sanelli
EPA Project Manager
EPA Community Involvement Coordinator
999 18th Street, Suite 300
999 18th Street, Suite 300 (80C)
Denver, Colorado 80202
Denver, Colorado 80202
303-312-6723
303-312-7822
Email: sanelli.diane@epa.gov
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Add Your Name To EPA’s Mailing List
If you would like to hear more about EPA
activities in this area,
please return the following coupon or email it to Diane Sanelli.
Name:
Address:
Affiliation
Phone #:
------------------------------------------------------------------------------------------------ EPA’s Ongoing
Investigation of Groundwater: Second Round of Sampling Results
Volume I Issue 2
March 2005
What Is EPA Doing?
The U.S. Environmental Protection Agency (EPA)
began an environ-mental investigation in the area around
Interstate 25 and Logan Street in Denver during the Fall of
2004. The specific area lies between Kentucky and Mississippi
and a few blocks to the east and west of Logan Street.
The primary purpose of the investigation is to determine if
there is ground-water contamination under residential or
commercial buildings and if it might pose any potential health
risk to nearby residents. The contaminant of most interest is
trichloroethylene (TCE), used mainly as a solvent to re-move
grease from metal parts. TCE can move from groundwater through
soil and as a vapor enter buildings, usually through cracks or
openings in the foundation slab or a crawl space.
What Did EPA Find?
Initially, EPA found that groundwater sampling
from 15 of 16 locations did not detect TCE in the shallow water
at approximately 33 feet. Subsequent sampling from deeper
groundwater below a clay layer from one location (north of 1-25
and on the east side of Logan Street) detected TCE at a level of
910 micrograms per liter or parts per billion (ppb). EPA
collected additional samples in that area in deeper wells at
approximately 45 feet. Results show a high level of TCE
(approximately 500 ppb) in one well. Al-though the groundwater
is not used for drinking water, these levels are well above the
established federal and State of Colorado drinking water
standard of 5 ppb.
EPA then installed more deep wells both north and south of 1-25
to deter-mine the extent of the contamination and determine if
any threat to residents may exist. A total of 27 wells, both
shallow and deep, have been in-stalled, Of those, 3 deeper wells
on Logan Street between Buchtel and Kentucky have shown TCE
levels ranging from about 500 ppb to 1,000 ppb. The deeper wells
east and west of Logan Street have shown only low levels from 3
ppb to 20 ppb.
What Did EPA Find? No Health Threat to Residents
In addition, a clay layer that exists in this
area has been observed in all EPA wells. It separates the
shallow from the deeper groundwater and appears to be acting as
a barrier, keeping the contamination from migrating to the
shallow groundwater. No significant groundwater contamination
was found at more shallow depths.
Based on these sampling results, we do not believe that
homeowners’ health and indoor air is being impacted by the
groundwater contamina-tion present in this area.
What Will EPA Do Next?
EPA will continue to investigate the extent of the higher levels
of TCE found along Logan Street. If we find contaminated
groundwater at shallow depths under residential areas, we will
conduct sampling in the home, as appropriate, to determine if
there are vapors directly underneath the foundation and if
indoor air sampling is warranted.
Give Us A Call!
Steve Way
Peggy Linn
EPA Project Manager
EPA Community Involvement Coordinator
999 18th Street, Suite 300
Denver, Colorado 80202
999 18th Street, Suite 300 (80C)
303-312-6723
Denver, Colorado 80202
303-312-6622
Email: linn.peggy@epa.gov
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Colorado
Department of Public Health and Environment
Trichloroethylene (TCE)
Health Effects Fact Sheet
January 2005
Reducing Exposure to
Trichloroethylene
Trichloroethylene (TCE) is one of a group of chemicals known as
volatile organic compounds, which readily evaporate at room
temperature. It is a chlorinated solvent that is of concern as
an air pollutant, a water pollutant, and as a substance
frequently present in ground water as the result of industrial
operations. TCE is a non-flammable, colorless manufactured
liquid with a somewhat sweet odor and a sweet, burning taste. It
is used as an industrial cleaner in the automotive and metals
industries. It also is found in many common consumer and
household products. Prior to 1977, TCE was used as a surgical
anesthetic, so the medical community has a substantial body of
knowledge regarding the health effects of TCE exposure in
adults.
How Could TCE Get Into My Home?
The presence of TCE in the home may be the result of historic
disposal practices of industrial wastes, or it may come from
other sources, such as household products that contain the
chemical. TCE can enter a building when it has been discharged
into the environment through spills and leaks that contaminate
surface water, soil or ground water. It’s vapors quickly
evaporate from surface water or surface soils in outdoor air,
posing no danger. TCE vapors can move through the soil and into
buildings, migrating through cracks in foundations, crawl spaces
or air space around pipes. Indoor air tests conducted by
specialists can determine whether occupants are being exposed to
air-born TCE.
TCE is found in products including typewriter correction fluid,
paint removers, paint strippers, gun cleaning fluid, cleaners
for electronic equipment, rust removers, adhesive glues, spot
removers, and other types of fluids. These products can emit TCE
into the air during their use and even during common household
storage. Exposure to TCE can be avoided by checking labels
before purchasing products and determining whether a
solvent-free alternative is available, or removing products that
contain TCE from the home. The requirements for product labeling
are not as stringent as those for food and drugs, so you may not
find TCE as a listed chemical. Try to use products that might
contain solvents out of doors when possible, or at least in a
well ventilated area. Additional information on chemicals in
household products can be found at the National Institute of
Health’s Web site
http://householdproducts.nlm.nih.gov/products.htm.
The primary ways people are exposed to TCE are through breathing
or ingesting. However, if you are exposed to TCE, many factors
will determine whether you will be harmed. These factors include
the dose (how much), the duration of exposure (how long), and
the pathway of exposure to TCE (breathing, ingestion, skin
absorption). In addition, other factors that must be considered
include exposure to other chemicals, age. gender, diet,
lifestyle, general state of health, and sensitive populations.
Draft TCE Health Risk Assessment
(EPA 2001)
EPA has recently completed a draft assessment of the health
risks posed by TCE after reviewing the available data since
1989(EPA 2001 at
http://cfpub.epa.gov/ncea/cfm/recordisplay.cfm?deid=23249).This health risk assessment is intended to replace a previous TCE health risk assessment conducted in the 1980s. The draft
assessment has been formally reviewed by the EPA’s Science
Advisory Board and had a public comment period. The EPA, with
support from the National Academy of Sciences, will prepare a
response to the Science Advisory Board comments. The draft
health risk assessment indicates TCE poses a higher risk for
sensitive populations than previously understood. In particular,
the cancer toxicity values that define protective levels of
exposure to TCE over a lifetime are significantly more
conservative than the previous numbers. As a result, the
Colorado Department Public Health and Environment has lowered
its health screening and clean-up action guidelines for TCE.
Major Findings of EPA’s Draft Health Risk Assessment (EPA 2001)
• Cancer effects - EPA concludes that TCE is "highly likely” to
cause cancer in humans. This cancer classification is supported
by increased risks seen in TCE-exposed workers to various
cancers, including cancer of the kidney, liver, lymphatic
system, prostate and cervix. Additional support is provided by
notable similarity between tumors in lab animals and in workers
exposed to high levels of TCE.
• Noncancer effects - While noncancer effects of TCE exposure
are unlikely, TCE can have a significant impact under certain
conditions. It can affect the
central nervous system, immune system, secretion system, organs
such as the liver and kidney and fetus development. EPA has
derived a reference concentration (RfC) of 40 micrograms per
cubic meter of air (parts per billion per cubic meter), based on
the critical effects in the central nervous system. liver and
secretion system. A reference concentration is the concentration
in air below which non-cancerous harmful effects are unlikely
applied to lifetime (30 year) human environmental exposures,
including to sensitive populations.
• Sensitive individuals - EPA predicts that sensitive
individuals or populations may be more at risk to TCE exposures
than an average individual. Sensitive individuals include
infants and children, and those with certain diseases (e.g.,
diabetes), lifestyle factors (alcohol consumption), and higher
exposures from other sources.
• Impacts of other exposures - Exposure to certain chemicals
other than TCE were found to increase TCE toxicity, and
vice-versa.
• Measuring cancer risks - While the link between long-term
exposure to TCE and cancer appears strong, there are many
uncertainties in the current ability to measure cancer risks to
humans. EPA included a range of cancer probability in its draft
assessment. At this time, using the most protective end of EPA’s
cancer factor range is a reasonable choice to protect sensitive
populations.
New Interim Policy for TCE Screening and Cleanup
Federal regulatory standards, called Maximum Contaminant Levels,
have been established for TCE in water. Because there is no
established national standard for TCE in air, the Colorado
Department of Public Health and Environment in August 2004
established a new interim policy revising screening and clean-up
levels for TCE. The state of Colorado uses a calculated
risk-based level to determine when action may be taken to
prevent residential exposure to TCE. The most protective end of
the cancer factor range is based upon a residential exposure
scenario in which a person theoretically is exposed to TCE for
24 hours-a-day, 350 days a year for 30 years (including 6 years
of exposure as a child and 24 years as an adult).
The Colorado Department of Public Health and Environment’s
interim policy is intended to provide guidance for risk
management decisions at Colorado sites subject to the
Department’s regulatory authority. Under the new interim policy,
risk screening will use the most protective level of 0.016
micrograms/parts per billion per cubic meter of air and may
involve indoor air testing. This screening level is based on a
risk level of one additional cancer in 1,000,000 people. If TCE
levels in a home range from 0.8 to 1.6 micrograms/parts per
billion per cubic meter of air, the Colorado Department of Public Health and Environment
intends to conduct further study to determine the source(s) of
contamination and whether remediation will be required. Sources
could include groundwater or emissions from household products.
Due to the uncertainty associated with ongoing evaluation of TCE
health risk assessment, the Colorado Department of Public Health
and Environment will continue to use the standard of one
additional cancer in 10,000 people as the maximum acceptable
risk.
Remediation of TCE
If TCE levels meet or exceed 1.6 micrograms per cubic meter of
air, and the levels are attributable to an environmental source,
the party responsible for the contamination may be required to
provide a ventilation system for the home. This involves the use
of relatively simple fan and vent systems that draw air from
beneath the building and prevent vapors from ever entering the
structure. This is the same method used to effectively remove
radon from buildings.
For More In formation About TCE:
Colorado Department of Public Health and Environment
Hazardous Materials and Waste Management Division
4300 Cherry Creek Drive South
Denver, CO 80246
Marion Galant Cathy Schuster
Community Involvement Manager Community Involvement Specialist
303-692-3304 303-692-3308
marion.galant@state.co.us
cathy.schuster@state.co.us
Redfield Site Cherokee/Gates and Gates Sites
Walter Avramenko
Unit Leader
303-692-3362
walter.avramenko@state.co.us
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DENVER
POST ARTICLES |
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FRIDAY,
MARCH 4, 2005
THE DENVER POST
DENVER & THE WEST
Gates sees
dramatic results in plume-cleanup bid
Neighbors of the ex-rubber plant attend a community
meeting and say they still want regular updates on the
TCE cleanup.
By Kris Hudson
Denver Post Staff Writer
Gates
Corp.’s initial experiments last month with a method of
eradicating a contaminant at its former rubber-plant
site in Denver yielded dramatic results.
Yet some neighbors remain concerned that Gates must be
held to its pledges to clean up the site. The Denver
City Council in December granted Gates’ request to
rezone the 30-acre eastern parcel of the site on South
Broadway. The change will make the parcel easier for
Gates to sell to an as-yet-unidentified buyer for
re-development.
At the time, some council members and neighbors keyed on
Gates’ pledge to begin removing trichloroethylene, or
TCE, from the site by January. TCE, an industrial
solvent, can cause headaches, lung irritation and
dizziness if breathed in small amounts. The state limit
for TCE in groundwater is five parts per billion.
Since January, Gates has experimented with methods of
removing a TCE plume from the site, said Tom Reeve,
Gates’ director of corporate development. A recent test
involved injecting into the ground a solution of
iron-infused carbon molecules that absorbed the TCE
particles and broke them down.
The result: After applying the iron-carbon solution to
an area with a TCE level of 52,000 micrograms per liter,
the reading dropped to 100 micrograms per liter, Reeve
said. Gates will monitor the effects of the test for a
few more weeks before deciding if it can be used to
clean the entire site.
“We hope to have a site wide remedy implemented by May,”
Reeve said Thursday.
Even so, neighbors and Councilwoman Kathleen MacKenzie,
whose district includes the Gates site, want continual
updates on the cleanup. MacKenzie convened a community
meeting attended by about 75 people at the Platt Park
Senior Center on Thursday to discuss it.
MacKenzie noted that Gates did not apply for inclusion
in the state health department’s voluntary cleanup
program until this week.
“I’m very relieved that they’ve done so because I think
people were concerned that Gates was not doing what it
said it would do at the rezoning hearing,” MacKenzie
said.
The 30-acre eastern parcel at the Gates site is separate
from a 50-acre parcel to the west, which Gates told to
Cherokee Investment Partners in 2001. Cherokee is
cleaning up TCE on that site in preparation for
redevelopment.
Staff writer, Kris Hudson can be reached at 303-820-1593
or khudson@
denverpost.com.
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December 12, 2004
Tests near Gates plant yield one site over TCE limit
By The
Denver Post
The U.S. Environmental Protection Agency’s recent
testing of groundwater in neighborhoods adjacent to the former Gates
Corp. rubber plant in Denver yielded only one reading of
trichloroethylene above state-allowed levels.
EPA representatives told a committee of the Denver City Council on
Wednesday that groundwater tests at more than 16 adjacent to the
Gates campus produced one high reading of TCE. That reading, at a
site north of Interstate 25 and on the east side of Logan Street,
showed 910 micrograms per liter, far above the state limit of 5 per
liter. TCE, a solvent, can cause nausea and dizziness if inhaled.
Gates reported high levels of the solvent in the groundwater on its
13-acre campus, which will be cleaned up before it is redeveloped.
Johanna Miller, the EPAs on-scene coordinator, said the agency will
continue testing. |
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Here are a few superficial notes taken
at the March 3rd meeting:
Type of test wells drilled (ground is dry down to about 25
feet)
1. Shallow wells (in the top of the water
table) 30-35 feet
2. Deep wells (to the bottom of the
water table) 35-40 feet
TCE is usually
concentrated at the bottom of the water table.
3. Drill into the bedrock
Methods of TCE
cleanup being used at the Cherokee and Gates sites.
1. Air Spurge & Vapor Extraction=bubble
air into the bedrock and extract the vapor.
Cherokee has
extracted 700 pounds or 55 gallons of TCE using this method on
their site.
2. Molasses=supplies food for the
biomass in the ground resulting in breakdown of TCE into
"daughter products"
which includes
ethane and various chloride compounds (one being vinyl chloride)
Cherokee is using
this method offsite to decontaminate the TCE plume
extending into the West Washington Park
neighborhood via
the ground water.
3. Carbon Molecules infused with Iron
Molecules=They fuse with the TCE and cause them the
breakdown into "daughter
products" (chloride
compounds)
Gates East is using
this compound in 3 wells to test its effectiveness.
Results: Well #MW7 which initially had 52,000 micrograms per liter TCE,
now shows 100 micrograms per liter (as
of March1)
Well #PZ02 which initially had 15,000
micrograms per liter TCE, now
shows 20 micrograms per liter
Well #PZ01 which initially had 45,000
micrograms per liter TCE, now
shows 15 micrograms per liter
The results look promising. This method will be used in more
wells onsite if tests reveal that it is working.
4. Potassium Permanganate=is an
oxidation chemical used on the Cherokee site.
For more complete and authoritative information on the cleanup
methods please see: Remediation
Techniques
TCE was discovered by the Colorado Department of Transportation
(CDOT) at Logan & Mississippi when they installed the tunnel
under Mississippi to drain I-25 during storms. The latest tests
show no TCE. There is speculation that because CDOT pumped
a million gallons of ground water each day during construction,
that the TCE was sucked backward temporarily from the Gates East
site.
Test wells drilled:
See maps
below
Cherokee has drilled 89 wells on and off the site.
Gates East has drilled 23 wells and 50 "grab samples"...Well
MW7 had 52,000 micrograms per liter TCE (5 micrograms per
liter is the EPA liter is the EPA standard). Gates entered the Voluntary
Cleanup Program on March 2nd.
EPA drilled wells along Mississippi and on the postal
property=TCE was non-detectable.
A deep well at Kentucky and Pennsylvania
showed TCE but at a depth that prevents vapor intrusion.
An off site well to the East of Gates (in
the area where I-25 and Logan meet) showed TCE.
We will post more complete information as we get it. If anyone
has more comprehensive details or corrections, please share them with PPRC and
we will share them with everyone. |
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Cherokee/Gates Toxic
Contamination Maps |
2004
GROUNDWATER
SAMPLING RESULTS IN THE
WEST WASHINGTON PARK
NEIGHBORHOOD.
The yellow line shows the extent of the plume of
TCE that migrated in the groundwater from the Cherokee site.IMPORTANT NOTE:
The new
Colorado state standard for TCE is 5 micrograms/liter so any amount
above that requires attention/cleanup. |
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MW-04
micrograms/liter |
| TCE: |
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34 |
| cis-1
.2-DCE: |
|
3.1 |
| 1.1-DCA: |
|
2.5 |
|
Chloroform: |
|
1.4j |
| SVOCs: |
|
ND |
| Metals: |
|
ND |
|
MW-06 |
| TCE: |
|
3.7 |
| Mercury: |
|
0.36 |
| PCBs: |
|
ND |
|
MW-03 |
| TCE: |
165 |
190 |
| cis-1.2
DCE: |
5 |
3.7 |
|
Chloroform: |
1.4j |
ND |
| Chromium |
44.5 |
ND |
|
GMW-2 |
| TCE: |
1090 |
2700 |
|
1.1.1-TCA: |
ND |
7.5 |
| 1.1-DCE: |
ND |
2 |
| PCE: |
ND |
4.1 |
| Metals: |
ND |
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MW-08 |
| TCE: |
|
1800 |
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MW-07 |
| TCE: |
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52000 |
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1.1.1-TCA: |
|
430 |
| PCE: |
|
120 |
| 1.1-DOE: |
|
70 |
| Toluene: |
|
6.7 |
|
MW-1O |
| TCE: |
|
3.1 |
|
MW-O1 |
| VOCs: |
|
ND |
| SVOOs: |
|
ND |
| Metals: |
|
ND |
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GMW-5 |
| Well is
dry; |
|
ND |
|
MW-11 |
| TCE: |
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5.1 |
|
BH-02A |
| PCBs: |
2' - 3' |
ND |
| VOCs: |
|
8' -
10' |
| TCE: |
|
2.2 ug/kg |
|
MW-02 |
| TCE: |
13700 |
1400 |
|
1.1.1-TCA: |
33.9 |
ND |
| PCE: |
21.6 |
4.4 |
| Carbon
Tet: |
4.7 |
ND |
| 1.1-DCE: |
4.5 |
ND |
| Toluene: |
3.4 |
ND |
| PCBs: |
|
ND |
|
MW-09 |
| TCE: |
|
500 |
|
GMW-4 |
| TCE: |
|
76.2 |
|
Chloroform: |
|
2.9 |
|
Metals+tin: |
|
ND |
| Cyanide: |
|
ND |
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MW-05 |
| TCE: |
|
1.0j |
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Chloroform: |
|
3.4 |
|
Metals-tin: |
|
ND |
| Cyanide |
|
ND |
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2004 TEST WELLS on the GATES EAST
CAMPUS Well values are listed in the
column to the left
IMPORTANT NOTE:
The new
Colorado state standard for TCE is 5 micrograms/liter so any amount
above that requires attention/cleanup. |
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