United States
Environmental Protection
Agency
Office of
Emergency and
Remedial Response
E PA/ROD/R06-89/048
March 1989
Superfund
Record of Decision:
-------
50272.101
REPORT DOCUMENTATION 11. REPOATNO. 12-
PAGE EPA/ROD/R06-89/048
3. A8cIpIenc'8 A~ No.
4. Tille and Subfl8
SUPERFUND RECORD OF DECISION
South Valley/Edmunds Street, NM
Fifth Remedial Action - Final
7. Author(8)
5. A8part 0818
03/30/89
I.
L Pwfotmlng Org8nlzdon Rapt. No.
8. Pwtormlng Org8lnlzatlon H8nw IIIId AddI'888
10. flqj8ctlT88IIIW0ItI UnIt No.
11. ~C),. Gr8nt(Q) No.
(C)
(G)
12. ~ Org8lliDllon H8nw and AdIh..
U.S. Environmental Protection
401 M Street, S.W.
Washington, D.C. 20460
13. Type of Rapor16 PerIod Covered
Agency
800/000
14.
15. Supplemanl8ry No...
11. Abatract (Umlt: 200 _1d8)
The South Valley/Edmunds Street site is a portion of the South Valley S~perfund site - a
large area in the southern part of the city of Albuquerque, New Mexico. The South
Valley site surrounds a city municipal water well identified as San Jose-6. Within this
larger area are a number of industrial properties owne~ and operated by different groups
and individuals. The site has been divided into operable units to address soil and
ground water contamination resulting from current and historical industrial practices.
The operable units include Edmunds Street Ground Water, Former Air Force Plant 83/GE,
San Jose-6, and the final operable unit, Edmunds Street Source Control. Potential
sources of ground water contamination within the Edmunds Street property have been
identified, but primary focus has been given to a drainage pit area -which receives most
of the drainage from the property. Investigations in all of the suspected potential
contaminant source areas, however, revealed little soil contamination. Even if further
migration of contaminants to ground water occurs, the ground water treatment system
developed in the previous Edmunds Street Ground Water operable unit will be sufficient
to address these concerns. There are no contaminants of concern affecting the soil at
this site.
(See Attached)
17. Document Analyat8 .. D88cr1ptol8
Record of Decision - South Valley/Edmunds
Fifth Remedial Action - Final
Contaminated Media: None
Key Contaminants: None
Street, NM
b. Idandfler8lOp.n.Ended Tanna
Co COSA TI FJeld/Group
18. Availabilty Statement
18. Secuity Cia.. (Th18 Report)
None
20. SecurIty Cia.. (Thla ""118)
Nnn~
21. No. of Paeaa
40
I
22. PrtC8
(See ANSl-Z38.18)
SH/mtrucdom on ~...,..
272 (4-71¥
(Fonn8fIy NTlS-35)
-------
EPA/ROD/RO 6-8 9/0.48
South Valley/Edmunds Street, NM
Fifth Remedial Action - Final
16. Abstract (continued)
The selected remedial response for this final operable unit is no further action.
Based on sampling data, the soil has been determined to contain contaminant levels
below hazardous contaminant concentration limits and poses no risk to human health
or the environment. The only further activities anticipated at the site are
sampling of soil gases in the drainage pit area following the ground water remedial
action, and the precautions necessary to prevent any disturbance of drainage pit
soils during the ground water remediation. There are no remedial or O&M costs
-------
v
.'
RECORD OF DECISION
EDMUNDS STREET PROPERTY SOURCE CONTROL
SOUTH VALLEY SPERFUND SITE
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
REGION SIX
.;
MARCH 1989
.n
. - - --
-------
DECLARATION OF THE RECORD OF DECISION
SITE NAME AND LOCATION
South Valley site, Edmunds Street Source Control Operable Unit
Albuquerque, New Mexico.
STATEMENT OF PURPOSE
This decision document outlines the remedial decision for the
Edmunds Street Source Control Operable unit in accordance with
the Comprehensive Environmental Response, Compensation and
Liability Act of 1980 (CERCLA), as amended by the Superfund
Amendments and Reauthorization Act of 1986 (SARA), and to the
extent practicable, the National oil and Hazardous Substance
Pollution contingency Plan, 40 CFR Part 300, November 20, 1985.
The State of New Mexico (through the New Mexico Environmental
Improvement Division) has been provided an opportunity to comment
on the remedial decision proposed by this Record of Decision.
STATEMENT OF BASIS
This decision is based on the administrative record for the South
Valley site, Edmunds street Source Control Operable unit (see
Attachment 1). The attached index identifi~s the items which
comprise the administrative record.
DESCRIPTION OF REMEDY
The Environmental Protection Agency has decided that no additional
action is necessary. It should be noted that a system for
groundwater extraction with surface treatment was specified in
the June 28, 1988 Record of Decision for the Edmunds Street
Groundwater Operable unit to deal with the contaminated.
groundwater under this property. Additional activities
that need to be taken are as follows:
1) Soils in the area of the drainage pit should remain undisturbed
for the duration of the groundwater remedial action. The area is
shown in Figure 1. A contingency plan will be developed with
precautions to be implemented should the soils be accidentially
disturbed during this period;
2) Following the completion of the groundwater remedial action,
soil gases in the drainage pit area should be sampled to
determine if the remaining levels pose any threat to human health
or the environment.
....-h_-._- .
. ."- " -.. . - ~
DECLARATION
This decision is consistent with the Comprehensive Environmental
Response, Compensation, and Liability Act of 1980 as amended by
-------
the Superfund Amendments and Reauthorization Act of 1986, and the
National Contingency Plan. It, in light of the previously
approved Groundwater Operable unit Remedial Action, is protective
of human health and the environment and attains Federal and State
requirements that are applicable or relevant and appropriate.
The New Mexico Environmental Improvement Division has been
consulted on this remedial decision and concurs with this
decision for the Source Control Operable unit (Appendix 2). The
above described action will be conducted in conjuction with the
remedial activities specified in the June 28, 1988 Record of
Decision for the Groundwater Operable Unit.
~
RKdi! ~~oi£¥it
Regional Administrator
March 30. 1989
Date
..- . .- -. - -....
.------
-------
L
o
s:::
0-
~
o
(I)
J.
J.
..
)
I
...
r:
...
()
CI
(
...
c-.
~----U--f)
J
I
I
/ DA-'
I .
I ::: t ~..CII FWd .. /'T-
I ). --~ ,/ , I
: ~ I
I .- L-L- .. 0Id- ---
I' , , 1 I Storage ANIle
I ' I Chemtca. r ~
I .. ,=....,\~~, \ \. V~
I .., I -" .. 1-,,\ \ ~1\'\ \~, \
tit) 8 !l "., ..\."
I.. - -- PiAiiiBoo.ooAii" FiioCE(i;E- - --:--
8Y-to
Ar..
FIGURE 1
Mort" L..e" Field
Ar.. --
~
-
.
.
I~
4r)
.
'0
C
::J
E
'Q
I1J
~
-------
TABLE OF CONTENTS
DECLARATION FOR THE RECORD OF DECISION
SUMMARY OF REMEDIAL ALTERNATIVE SELECTION
SITE LOCATION AND DESCRIPTION
CURRENT SITE STATUS
SITE RISKS
ENFORCEMENT ANALYSIS
COMMUNITY RELATIONS
OPERABLE UNITS
SELECTED REMEDIAL APPROACH
OPERATION AND MAINTENANCE
FUTURE ACTIONS
. SIGNIFICANT CHANGES IN THE SELECTED ALTERNATIVE
TABLE 1 - SOIL SAMPLING RESULTS
APPENDICIES
APPENDIX 1
ADMINISTRATIVE RECORD INDEX
APPENDIX 2
STATE OF NEW MEXICO CONCURRENCE
.
..
APPENDIX 3
RESPONSIVENESS SUMMARY
FIGURES
FIGURE 1
AREAS OF RESTRICTED EXCAVATION
FIGURE 2
SOUTH VALLEY SITE
FIGURE 3
EDMUNDS STREET PROPERTY POTENTIAL CONTAMINANT
SOURCE LOCATIONS
;v
i
1
1
3
3
4
4
5
5
7
7
7
8
iii
.- 1 -
-------
SUMMARY OF REMEDIAL ALTERNATIVE SELECTION
South Valley, Albuquerque, New Mexico
Edmunds Street Source Control operable Unit
Site Location and Description
; .
The Edmunds street property is a portion of the South Valley
Superfund site in Albuquerque, New Mexico. The South Valley
Superfund site is an area surrounding the City of Albuquerque
Municipal Water Well known as San Jose 6, near the intersection
of Broadway and Woodward Road in southern Albuquerque. The
Edmunds Street property is located at 3301 Edmunds Street.
Figure 2 below shows the larger South Valley site with the
Edmunds Street property in the southeastern corner of the site.
Figure 3 on the next page shows the Edmunds Street property in
more detail.
! ~:
...-::
. ..
FI GURE 2
SOUTH VALLEY
SITE DETAIL
.. - .
. -
."",8.
-... -.
j
"]n;~J
, . , - = ';, ~ ,/"--,.=-=,-,-, ., ..,..," ..
~. ; === - , ,;' i !;;-l_n'~ ","iTflHO
. -- .;" L_~ J' .
. . . I . , L.
. " ~ ,~" ...:.,.,.,.:=::;;. ,,:-~ , ._,~ 5'-6 w~1I '
i .. = T[r~l{iJ(:!T== -- ! '
_I. lilt I d~
, - 01
. . -. ]'~O]/'; 8O'.iirl ;
, ~....g
. I J ' I Co. .
I..J. "" ;
! 1c:~'JO , , ~ ~~! sJ
== '~~-:~"L i
- --.; '--1 - ---::. -
o PRP Properties
..'
:
---..- -: - --
Edmunos 51.
'P~les
r ;Li
I' .
L_--1
. .. "...
-.- . - -."
. .......-----------..
---.-------.
-------
- -.
..
Figure 3 sho~s ~he var:~us Fcten~ial sc~~=es c: c~nta~:~a~:c~
within the Ed~~nds S~ree~ P~oFe~~y. These include the d~a:nage
pit area, the sep~ic tank d~ain fields, the tank :ar~, and the
cld dru~ storage areas. 7he a~ea aroun= ~onitor:ng well SV-IO is
called the drainage pit area. This area is a low spo~ on the
property and much of the drainage for the property flows to this
spot. The east and west leachfields are for.the septic tanks
located in conjunction with the property buildings. The tank
farm area contains above ground tanks used for product storage.
Finally the old drum storage areas were once used for the storage
of drums of chemicals. All of these areas were investigated as
potential sources of contamination, but the primary focus was on
the drainage pit area.
GM-17B
GM-16
North L..cll Field
Ar..
r----cr--.
,
,
,
I
,
'West leach ReId TF.NW
Area ~
, 18 ;.--. I I
" Q TF\ 10Id~ ~' ---
1 Storage Area.
I I Chemical f) 7 .6 \L5__-
I Storage
, - 8 GM-3 . I :;~: e GM- , -~ - . 1 ----
- I "8 rt. 3 e 9 GM- 9 e
~ GM-1~ ~...:-:. '$ S8-1- - ~M-4-~_- TFS~" 4~ ..10
PlAHT BOUH'DARY FENCE L"E 111
GM-
TFNE
GM-2
-
.
.
I ::
~
.
o
C
::I
E\
~ .
wI
SV-10
Are.
POTENTIAL SOURCE AREAS
FiGURE 3
-------
Current Site Status
After the existance under the site of groundwater contamination
as high as the part-per-million level of chlorinated organic
solvents was revealed, a search for the source of this contamination
was launched. The results of the final phase of this search can
be seen in Table 1. Nineteen soil borings were taken in all of
the suspected potential contaminant source areas. In the area of
suspected greatest contamination, the drainage pit, these samples
extended from the surface to the water table more than 100 feet
below. Little soil contamination was found. Of the 142 soil
samples taken only eleven indicated part-per-billion level
contamination. These eleven samples were concentrated in three
areas: soil boring SV10-3, samples from soils in direct contact
with contaminated groundwater, and the northern part of the tank
farm area. The contamination in boring SV10-3 was found in four
samples and consisted of a single contaminant, tetrach10roethene, at
levels from 80 parts-per-bi11ion to nondetectable levels. This
differs from samples taken between 1978 and 1985 which did
indicate the presence of higher levels of solvent contamination
in the drainage pit area. This difference is likely the result
of the continued migration of solvents from the soils down into
the groundwater. This is supported by groundwater sampling data
which show contamination levels directly beneath the pit have
fallen from 22,900 parts-per -billion (ppb) total volatile organic
compounds in 1985 to 872 in 1988. The contamination found in
samples from soils that are in direct contact with the
groundwater reflect the contamination found in the groundwater
rather" than the soil. This contamination will be remedied
through groundwater treatment. The three soil samples which
showed contamination in the tank farm area had levels of 118, 21
and 14 ppb. These results point to minor suerface spillage
associated with operation of surface tanks and not a potential
continuing source of contaminants to groundwater that was the
object of the investigation. Even taking the worst case,
assuming that the full area of the most extensive contamination
around boring SV10-3 is contaminated to the full 25 foot radius
between SV10-3 and th clean borings, there could only be a
maximum of 60,000 cubic feet of contaminated soil. This is not
enough to pose any risk of continued groundwater contamination.
Even should there be further migration of contaminants to
groundwater, it will be cleaned"up through the groundwater
treatment system already "selected.
site Risks
The soils pose no risk to human health or the environment. The
three primary routes of exposure thro~gh which the public could
be exposed to contaminated soils are direct contact, ingestion of
contaminated soils, or inhalation. What little soil
contamination was found is below the surface. There is no risk
of direct contact. Should, in some improbable manner, these n
soils be exposed, even daily ingestion of 100 mi11ligrams of the
contaminated soil over a lifetime would not pose a threat to
human health.
-------
The remaining route is inhalation. There is not enough
contamination remaining in the soils to sustain a continuous
release. But, to evaluate a worst case assuming the highest
concentration of the worst contaminant (30,000 micrograms per
cubic meter 1,1 dichloroethene) was somehow released all at once,
the maximum exposure would be approximately 0.7 micrograms per
liter (ug/l) 230 meters northeast of the drainage pit. The
standard for occupational exposure to this chemical is 20,000
ug/cubic meter. Though there is not sufficient contamination to
sustain a release for 70 years, the standard for lifetime
continuous daily exposure is 0.02 ug/cubic meter. Even given the
long chain of exteme assumptions that were made there is no
chance of the soil gases posing a risk. Air modeling shows that
the population most effected from air releases is 3/4 of a mile
(2000 meters) to the northeast. However, to eliminate any
possibility of these soil gases posing a threat, the Record of
Decision will contain a provision to prevent disturbance of the
soils until the contaminants can be removed from the underlying
groundwater. There remains the possibility of migration of
contaminants below detection limits into t~e groundwater.
However, the groundwater remedial action already selected calls
for collection and treatment of the groundwater from beneath the
site. This will provide a safety net to catch any potential
migration however unlikely such potential may be.
Enforcement Analysis
There is a list of several potentially responsible parties (PRPs)
for the Edmunds Street property. These include past and present
owners and operators of the property. The primary PRPs for the
purposes of this document are the UNIVAR Corporation through its
Van Water & Rogers subsidiary, and AmeriGas a previous property
owner. The UNIVAR Corporation has engaged in negotiations with
EPA for implementation of the groundwater remedy at this
property. Negotiations will be conducted to include the actions
required by this Record of Decision along with those required for
groundwater. These negotiations will be conducted with the
intent of reaching an agreement between the PRPs and EPA which is
enforceable in Federal District Court.
Community Relations
-
There has been some media interest in the overall. South Valley
Superfund site, but interest from individual citizens in the --
Edmunds Street property has been low. A citizens group, the San
Jose Community Awareness Council, has been formed and has
expressed interest in the South Valley Superfund site. This
interest included a letter of intent to apply for a Technical
Assistance Grant for the South Valley site.
Notice .ofEPA's proposed remedial decision was provided to
potentially affected persons through a press release on February
27, 1989 and was followed by a direct mailing in both English and
Spanish to individuals and groups on the site mailing list. The
mailing included a fact sheet describing the site problem and the
-------
proposed remedial decision. The public comment period on the
remedial decision ended March 28, 1989. A public meeting
on the proposed remedial decision was held on March 16, 1989 at
the East San Jose Community Center in Albuquerque. The meeting
was attended by approximately 30 individuals, two of whom had
questions about the proposed decision. All of the questions
asked were answered at the meeting. The response to comments
or questions submitted during the public meeting and during the
comment period is presented in the Responsiveness Summary at the
end of this document.
ODerable Units
The South Valley site has been divided into four operable units.
These are the Edmunds Street Source Control, Edmunds Street
Groundwater, Former Air Force Plant 83/GE, and the overall
Offsite portion also known as SJ-6. The division of the site
into these parts follows from the nature of the site. The South
Valley site is a large area surrounding the City well San Jose
#6. within this larger area are a number of industrial
properties owned and operated by different groups and
individuals. Each of the two source control operable units deals
with a single industrial property that through the investigation
process has been shown to have or to have had contamination that
requires action. The overall Offsite operable unit was intended
to deal with ~he site as a whole, leading to a decision about the
larger groundwater issues that caused this area to become a
Superfund site, while the source control operable units eliminate
the sources of groundwater contamination. The Edmunds
Groundwater operable unit dealt with a specific groundwater plume
originating on that property and extending to the east.
The Edmunds Street Source Control operable unit is the subject of
this document.' It is the last of the operable unit Record of
Decisions for this site.
SELECTED REMEDIAL APPROACH
No further action has been selected as the remedial decision for
the Edmunds Source Control operable unit. As mandated by the
Comprehensive Environmental Response, Compensation and Liability
Act of 1980 (CERCLA) as amended by the Superfund Amendments and
Reauthorization Act (SARA) of 1986 and in accordance with the
National Contingency Plan (NCP) several statutory requirements
must be met for selecting the appropriate remedial approach for a
Superfund site:
* Overall Protection of Human Health and the Environment
*. Consistency with Other Environmental Laws
* Cost Effectjveness
Based on the finding of no significant soil contamination during
the remedial investigation, EPA concludes that no further
remediation beyond that required in the June 28, 1988 Record of
Decision for the Edmunds Street Groundwater operable unit is
-------
warranted or necessary. Activities which are recommended and
will be included in the groundwater remedial activities include
protection of the soils in the drainage pit area from disturbance
during the groundwater cleanup and testing of soil gases in the
area following the groundwater remediation to insure that the
remaining gases pose no threat to human health and the environment.
As detai~ed in the remedial investigation report and shown in
Table One, no significant soils contamination remains. It is not
our claim that the soils are completely clean. They are not.
What we are saying is that what little contamination was found in
the soils poses no threat to human health and the environment.
There is one boring in the drainage pit area, boring SV10-J, that
shows one contaminant, tetrachloroethene (PCE), at levels from 80
parts-per-billion to nondetectable in the samples from that
boring. The six borings which surround SV10-J do not show this
contamination (see Figure Three).
It is likely that the migration of the contaminants into the under-
lying groundwater continued until the level of the contaminants
dropped below detection limits of the sample analysis methods.
The public is also protected from any potential migration of any
contaminants below the detection limit, however unlikely, by the
groundwater remedy. Any contaminants would migrate into the
groundwater below the site. This groundwater will be collected
and treated as part of the groundwater remedial action. The
absence of a continuing source of contamination in the soils is
supported by the most recent groundwater sampling data from
August and September 1988, which show a drop in the level of .
contaminants in the groundwater directly below the drainage pit
area. .
A. consistency with the National Contingency Plan and the
provisions of the Superfund Amendments and Reauthorization Act
This decision, in conjunction with the remedial action approved
in the June 28, 1988 Record of Decision, provides for protection
of human health and the environment. In addition, this decision
is consistent with the National Contingency Plan (NCP), 40 CFR
JOO.68(d) which requires the lead agency to gather sufficient
information to determine the necessity for and proposed extent of
remedial-action. Development of remedial alternatives was not
wa~ranted in this ~ituation on the following basis:
* As was explained above, no significant contamination was
detected in the Edmunds property soils, and thus no continued
risk to human health and the environment is posed by the site.
soils.
* The little contamination which was detected in the soils does
not exceed any Federal or State standards as there are none for
soil contamination. Examination of any threat posed by any
remaining contamination to human health or the environment showed
no risk either through ingestion or direct contact with the
subsurface contamination. The only potential for harm was
-------
through the remote chance of contamination of underlying
groundwater and its subsequent consumption. This potential was
dealt with in the June 1988 groundwater remedial decision.
The no further action remedial approach is, therefore, consistent
with applicable environmental laws.
* The soils themselves do not contain enough contamination to
warrant their remediation. The next "level of treatment would
involve a technology for removal of what little contamination
remains. Going to this next, more expensive level of technology
would not provide any additional protection to human health or
the environment as the only probable route of exposure, ingestion
of water contaminated through further migration of soil
contaminants, has already been remedied through the groundwater
extraction and treatment system selected in the June 1988 ROD.
The selected remedy is therefore ~n efficient use of resources.
Two other criteria are normally considered in the evaluation of
remedial alternatives. They are that the alternative selected
utilize permanent solutions and alternative treatment
technologies or resource recovery technologies to the maximum
extent practible and that the preference for treatment that
reduces toxicity, mobility, or volume as a principle element is
satisfied. As no significant levels of contamination were found,
there was no material to be treated eliminating both of these
criteria from consideration.
OPERATION AND MAINTENANCE
No operation and maintenance (O&M) is anticipated other than
insuring that site soils within the specified area remain
undisturbed during groundwater remediation.
FUTURE ACTIONS
The only future
in the drainage
insure that any
threat to human
action anticipated is the sampling of soil gases
pit area following groundwater remediation to
remaining contaminants in the soil gases pose no
health and the environment.
SIGNIFICANT CHANGES IN THE SELECTED ALTERNATIVE
There was no change in the recommended alternative as presented
to the public during the public comment period and at the public
meeting and that recommended alternative is. the selected
alternative.
..--.---...
-------
TABLE ONE
SOIL SAMPLING RESULTS
. - ..-- - .
-------
..
:
"!'
.,
}-
'J '
{
t
:
1
Summary of Vo:atl1e Orl&r.~c Compound Concentratlons Detected
Detectlon L~~t 1~ So~l SL~:eJ 1n the Vic~nity of the SV-10
3301 Edmunds Street Slte, Albuquerque, Nev Mexlco.
above the Contract Req~1red
Area, Collected April 1988,
lor1Da De.l&D&tlon:
Sulple IMerval:
Dau Sampl.d:
Work Order lumb.r:
Unlt. :
ISL
I.na.ne
bl.(Chlorometh,l).tbar
Ir_forlll
CarboD t.tracblorlde
OUorobena.n.
Chlorodlbromomethane
Cbl oro. tbaD.
2-Chloro.th,lyLn,1 .th.r
Chloroforlll
Dlchlorobromamethane
1.1-D1chloroethane
1.2-D1chloro.thane
trana-l.2-D1chloroethene
1.1-Dichloroethene
1.Z-Dichloropropane
c1a-l,]-Dichloropropylene
Ethy1ben.ene
Methyl bromide
Meth,l chlorlde
Meth,lene chlorlde
l,l.2.2-Tetrachloroethane
Tetrachloroethene
Toluene
1.2-tran8-D1chloroeth,len.
l,i,1-Tr1ch10roethane
Tr1chloroethene
Tc1chlorofluoromethane
Vinyl chlor1de
Acetone
2-Butanone
V1nyl acetat.
2-Se.anone
4-Methyl-2-pentanone
Styrene
Toul JrYlen..
$V10-1
, - 7'
4/6
58-04-040
SV10-1 $V10-1 5V10-1 $V10-l
10 - 12' 20 - 22' 30 - 32' 40 - 42'
4/6 4/6 4/6 4/6
58-04-040 58-04-040 58-04-040 58-04-040
(ua/lta) (ua/k.l) (ua/k.l) (uallta)
(ualkl)
--
11 IL
181L
11 IL
14 IL
I,lL
J
. Concentrat1ons less ~an the contract requlred detect10n lLm1t8.
Detected 1n realent ~lank.
Laboratory e8tLmated .alue, but could not be quantLf1ed.
Laborator, dupl1cate anal,sls.
Hazardous Sub.tance Llst.
Outslde laboratory callbratlon ranae.
M1crolrams per k11olram.
.
RSL
S
-------
v
'r
~r
~
f
f
~
1
t
S~ry of Vola~i:e Orlanic Compound Concentration. Detec~ed
~etec~ion L~it i~ Soil Sacples in the Vicini~y of ~he SV-IO
3301 Edmund. Street Site, Albuquerque, Mev Mexico.
above ~he Con~rac~ Required
Area, Collected April 1988,
--------Replica~e---------
lor1ne De.1Ina~1on; mO-l SVl0-l* SVl0-l SVl0-l SVl0-l SVl0-l
Sample In~erval: 50 - 52' 50 - 52' 60 - 62' 70 - 72' 80 - 82' 90 - 92'
Date Sampled: "6 "6 4/7 "7 '17 '/7
Wodl. Order J\llDher: 58-0'-0'0 $8-0'-0'0 58-0'-040 58-0'-0'0 58-0'-040 58-0'-0100
~1t.: (ua/!r.a) (ua/lr.a) (ua/!r.a) (ua/!r.a) (ua/!r.a) (ua/lr.a)
15L
"_.118
b1.(ChlorD88~h,1).tbar
Ir_fo1'8
Carbon C.~raeh1orlde
Chlorob.na.n.
Chlorod1br08G88~han.
Chloroe~hane
2-Chlor08~h7lY1n71 .U1er
Chlorofo1'8
D1chlorobromome~hane
l.l-D1chloro.U1ane
1.2-D1chloroe~hane
~ran.-l.2-D1chloroe~hene
1.I-D1ch1oroe~hene
1.2-Dichloropropane
c1.-l.3-D1chloroprop71ene
l~h71ben&.ne
Heth7l bromide
Keth,l ch10r1de
Meth,lene chlor1d. 6.9 IL
1.l.2.2-Tetrachloroethan.
T.~rachloro.~h.D.
To1uen.
l,2-tran.-D1chloro.~h7l.ne
l.l.l-Tr1chloroethan.
Trichloroeth.ne
Trichlorofluoromethane
V1n71 chlor1.de
Ac.ton. 151L lOlL 14 IL 151L 1llL
2-lutanon.
Vin7l acetate
2-Bexanone
'-He~h7l-2-pentanon.
5t7r.n.
Total xyl.n..
I,lL
J
Conc.n~ra~10n. 1... than the contrac~ required detec~10n 1~1~...
Detect.d 1n realent blank..
Laborator, e.t~ted value. but could not be quan~lfled.
Laboratory dupl1ca~e anal,.l..
Sa.ardoui Sub.tanc. L1.~.
.
BSL
S
ullkl
Outsid. labora~or7 calibr.tion ranae.
-------
L
.
p
r
~r
K
M8r
~
I
f
\
J
,'!"
5ummary of Vola~~:a Orlanl~ Compound Con~antra~lon. Dete~ted
De~a~~10n Li:it .~ So.: S~~:eJ ln ~he Vi~ln1ty 0: ~he 5V-10
3301 E4mund. S~re.t S1te, Albuquerque, Nev Kexl~o.
above ~he Contra~t Requlred
Area, Coll.~~ed Aprll 1988,
lorln& De.lIDation: SV10-Z SV10-Z SV10-Z SV10-Z 5V10-Z SV10-Z
5A111ple Innrval: S - 7' 10 - 1Z' ZO - ZZ' 30 - 3Z' 40 - 42' SO - 5Z'
Can 5A111plec!: 4/7 4/7 4/7 4/7 4/7 4/7
Work Orde r Jumhe r: 58-04-049 58-04-049 58-04-049 58-04-049 58-04-049 58-04-049
lJni~a: (ua/q) (ua/q) (ua/q) (ua/q) (ua/q) (ua/kl)
15L
leuene
bi.(CblorQ88~l)etb.r
Ir_fol'lll
CarboD tetrachloride
Cblol'obeGa.-
Cbloroc!lbr-tbaDa
ehloroethan.
2-ehlor08~h71.1ft71 .~her
Chlorofol'lll
Clch1orobromame~hane
l,l-Dl~hloroethane
l,Z-Dlchloroethan.
tran.-l,Z-Dlchloroethene
l,l-Dlchlor08thene
l,2-Dlchloropropane
cl.-1,3-DlchloroproP71en.
Eth71 benaene
tteth7l br_lde
M.th7l cModd.
Ke~h71ene chlorlde
l,l,2,2-Tetra~hloroethane
T.trachloroethene
Toluene
l,2-tran.-Dlchloroeth,lene
l,l.1-Trl~hloroethane
Trlchloroethene
Trl~hloro!luor~thane
Vln,l chlorlde
Acetone 1$ IL' 1$ IL 141L
Z-Butanone
Vln,l .~et.te
Z-Rexanone
4-Hathyl-2-pentanone
5tyrene
To~al xylene.
B,BL
J
Con~en~ra~lon. le.. ~han the con~ract requlred de~ec~lon l~lt..
Dete~ted Ln realent blank.
Laboratory ..tLmated value, but
Labora~ory dupllcate anal,.l..
Sarardou. 5ub.tance Ll.~.
...-...--
could not be quantified.
.
SSL
5
ul/l<&
Ou~.lde laborator7 callbratlon rAnle.
-------
~
[
. f
[..
.f
f
~
t-
J
Summary of Volatlle Orlanic Compound Concentratlo~ Detected above the Contract Requlred
Detection L~it l~ Soll S~les in the Vlcinity of the 5V-10 Area, Collected April 1988,
3301 Edmunds Stree: 51:e, Albuquerque. Nev Mexlco.
lorlae Deal,Dation: SV10-Z SV10.Z SV10-Z SV10-Z SV10-Z
Sample Interval: 60 - 62' 10 - 1Z' 80 - 8Z' 90 - 9Z' 100 - 102'
Dau Sampled: 411 411 411 411 411
Work Order lumber: 58-01-049 58-01-049 58-01-049 58-01-049 58-01-049
Unl~.: Cua/q) Cua/q) Cua/q) (ua/q) (ua/q)
ISL
Ie_ene
~laCCb1or088~yl).ch8r
Ir-fora
Carbon ~.~r.cblorlde
CblorobeQaene
Chlorodlbr_UI.afte
Chloroetbane
2-Chloroethylvinyl .~her
ChlorofoEm
Dlchlorobromamethane
1.1-Dichloroeth&ne
1.2-Dichloroethane
trana-l,Z-Dichloroethene
l,l-Dichloroethene
1.2-Dichloropropane
cla-1.3-Dichloropropylene
Ethylbenaene
Methyl br_ide
Methyl chloride
Kethylene chloride
1.l,2.Z-Tetrachloroath&ne
Tetrachloroethane
Toluene
1.Z-trana-Dlchloroethylene
1. 1. l-Trlchloroethane
Trlchloroethene
Trichlorofluoromethane
Vinyl chloride
Acetone 20lL' 20lL
2-Butanone
Vinyl acetate
2-Sexanone
4-Kethyl-2-pentanone
Styrene
Total ""lene.
.,BL
J
Concentrationa le.s than the contract required de:ectlon l~lta.
Detected 'in rea,ent blank.
Laboratory e.tLmated value. but could not be quantified.
Laboratory duplicate analy.l..
Sarardoua Substance Li.t.
.
B5L
S
ua/k,
Outside laboratory calibration ranae.
-------
Summary of Volatile Orlanic Compound Concentratlon. Detected
Detection LL=it 1~ Soil Sample. ln the V1cinity of the SV-10
3301 Edmund. Street Slte, Albuquerque. Nev Mexlco.
above the Contract Requlred
Area, Collected Aprll 1988,
II --------Replicate---------
" lorlna De.llnation: SVl0-' SVl0-' SV10-'. SVlO-' SV10-3 SV10-'
5Aq11e Inurval: ~ - ,. 10 - 12' 10- 12' 20 - 22' 30 - 32' 40 - 42'
k Dau Sampled: 4/8 4/8 4/8 4/8 4/8 4/8
Work Order lumber: 58-04-048 58-04-048 58-04-048 58-04-048 58-04-048 58-04-048
Unit.: (\&I/ILa) (\&I/ILa) (\&I/ILa) (\&I/ILa) (\I&/kl) (\&I/kl)
ISL
r "naene
bi.(ChlorD88th,l)etber
Ir-foE8
-~ Carbon tetrachloride
I Chlorobenaene
Cblorodibromaaethane
ChloroetNo.Ae
t. ( 2-Chloroeth,lyLn,l ether
Cblorofonl
Dichlorobromom8thane
l,l-Dichlor08thane
1.2-Dichlor08thane
_. tran.-l,Z-Dlchloroethene
1.1-Dichloroethene
1.2-Dichloropropane
ci.-l.3-Dichloroprop,lene
It.h,lbenune --
1 . "-th,l bromide
Meth,l chloride
Methylene chloride
1.1.2.2-Tetrachloroethane
1 . Tetrachloroethene 81 21 16 19 9.6
Toluene
1.2-tran.-D1chloroeth,lene
I 1. 1. 1-Trichloroethane
Trichloroethene
Trlchloro!luoromethane
Vin,l chloride
F Acetone 231L 13 IL 121L 211L 15 IL 221L
2-lutanone
r Vln,l acetate
2-Bexanone
4-Keth,l-2-pentanone
St,rene
~ . - Total .,.lene.
Concentratlon. r.ili-than the contr.ct required detection l1miu.
I,lL Detected in r.alent blank.
J Laboratory e.t1mated value, but could not be quantlfied.
. Laboratory duplicate an817.1..
BSL Ba&ardou. Sub.tance Li.t.
S Out.1de laborator, calibration ranal.
ul/.., Mlcrolram. per kilo,ram.
-------
~
[
~r
t
r
I
,
I -
t
Summary of Vola~~:e Orl&r.lc Compound Concentration,
De~ec~ion LWBi~ in Soi~ SAmple, in ~he Vicinity of
3301 Edmund. S~reet Si~e, Albuquerque. Nev Mexico.
Detec~ed above ~he Contract Required
~he SV-10 Area. Collected April 1988,
10rLna Desianation:
Sample Interval:
Data Sampled;
Work Order JYmber:
Units:
SVI0-3 SVI0-3 SVI0-] SVIO-] SVIO-] SVI0-3
50 - 52' 60 - 62' 70 - 72' 80 - 12' 90 - 92' 100 - 102'
"8 "8 "8 "8 "8 4/8
S8-0'-048 58-04-048 S8-0'-048 S8-0'-048 S8-04-048 58-04-048
(ua/ka) (u.a/ka) (ua/ka) (\aa/ka) (ua/ka) (ua/ka)
ISL
lena.ne
bis(CblorD88th,l)eth8r
Ir-fora
Carbon totrachlorido
Chlol'obenao-
Cbloro4!lbr-tb&ne
Cbloroethane
2-Cblorooth,lY1n,1 ether
ehlorofora
Dichlorobromameth&De
I.I-Dlchloroethane
1,2-Dichloroethane
trans-l.2-Dichloroe~hene
l.l-Dichloroethene
1.2-Dlchloropropane
cis-I,3-Dichloroprop,lene
E~hylben&8ne
Kath,l br-ide
Keth,l chloride
KethJlene chloride
l,l.2.2-Tetrachloroethane
Tetrachloroethene
Toluene
1.2-trans-Dlchloroeth,lene
1.1,I-Trlchloroethane
Trichloroethene
Trichlorofluor~thane
Vinyl chloride
Acetone
27 J
U BL
900
150
190
13 It.
16 It.
16 It.
15 I
5.400 8
2-8utanone
Vin,l acetate
2-Bexanone
160 J
'-Kethyl-2-pentanone
Styrene
Total xylenes
Concentrations le.s than the contract required detection lLDits.
De~ected in reaaent blank. .....--....
Laboratory est~ted value, but could no~ be quantified.
Laboratory duplicate analysis.
Hazardous Substance List.
8,8L
J
.
BSL
S
, ul/ka
J
Outside laboratory calibration ranae.
-------
I U
[
- f
e
c
J
L
F
1
I
r
1
Summary of Volati:e Orl~ic Co=pound Concentrations Detected
Detectlon Li=it i~ 50Ll Sample. in t~. VLcinlty of t~e 5V-10
3301 Edmunds Street Slt., Alb~querq~e, Mev Hexlco.
above the Contract Required
Area, Collected AprLl ~988.
.o~ln& Deai.nation: SV10-4 SV10-4 SV10-4 SV10-4 SV10-4 SV10-4
Sample Interval: ,s - 7' 10 - 12' 20 - 22' 30 - 32' 40 - 42' ,S2 - 's2'
Date S~lad: 4111 4111 4111 4111 4/11 4111
Wo~k Orde~ Jumbe~: S8-04-0,S4 S8-04-0,S4 58-04-0S4 58-04-0S4 58-04-0S4 58-04-0,S4
OnlU: (ua/q> (ua/q> (ua/q> (ua/q> (ualq> (ua/ka>
ISL
hnae-
~l.(CblorG88~l).th8r
.~_fonl
Ca~boa cec~achlo~lde
Chlo~obenaeMl
Cblorodlbr--cbane
Ch1oroethane
2-ChloroethylT1nyl .Cher
Cblorofonl
Dlchlorobromamethane
1.1-Dichloroethane
1.2-Dlchlorcetbane
tran.-l.2-Dichlo~o.thene
'l,l-Dichloroethene
1.2-Dichloropropane
c18-l.3-Dlch!oropropyle-
Ethylbenaene .
Huhyl br-ide
"ethyl chloride
"ethylene chloride
1.1.2,2-tetr8chloroethane
tetrachloroethene
tol~ene
l,2-trans-Dichloroethylene
1.1.1-Trlchloroethane
Trlchloroet~ene
Trlchlorofl~orometh&ne
Vinyl chlo~ide
Acetone 11IL 11IL !SI 16 I
2-lutanone
Vinyl acetate
2-Bexanone
4-Hethyl-2-pentanone
Styrene
Total xylene.
I.n
J
Concentratlons less than the contract required detection li=lt8.
Detected in realent blank.
. --- . ---..- -
*
Laboratory e.tLmated value. but could not be quantified.
Laboratory duplicate analy.is.
Harardous Sub.tance Li.t.
B5L
S
ualka
Out.lde laboratory callbratlon ranee.
-------
SummAry of Vola~i:e Orlenic Compound Concen~ra~ion. De~ec~ed
De~ec~ion L~i~ i~ 5011 S~le. in ~he Vic~~1ty of ~he SV-l0
3301 Edmw\ch S~reet Site. Albuquerque. Nev Mexico.
above ~he Con~ract Kequired
Area. Collec~ed Apr11 1988.
--------Kepllca~e---------
Iorlna De.llna~lon: SVl0-' SV10-' SV10-' SV10-' SV10-'. SV10-4
Sample Interval: 60 - 62' 70 - 72' 80 - 82' 90 - 92' 90 - 92' 100 - 102'
Date Sampled: '/11 '/11 '/11 '/11 '/11 4/11
~\ Work Order J\8bar: 58-0'-05' 58-0'-05' 58-04-054 58-04-054 58-0'-054 58-04-054
I. Unl~.: (\I&/ka> (\I&/k,> (\I&/ka> (ua/ka> (\I&/ka> (\I&/k,)
BSL
r lenaene
~1.(Cb10r088~11).~r
Ir-for8
Carbon ~a~rach1or1da
~ ~ Chloroba_ana
Chlorod1br_~hafte
Chloro.~hafte
[~ Z-Chlor08~hyl.Ln11 .~r
Chlorofor8
Dlchlorobr0mam8~
1.1-Dlchloroe~h&ne
l,Z-Dlchloroe~h&ne
~ran.-1,Z-D1chloroe~hene
....
l,l-Dichloroe~hene
l,Z-Dichloropropane
cl.-1,3-Dlchloropropylene
E~hylbenune
Huh1l br-lde
He~hyl chlorlde
IlL He~hylene chlorlde
l,l,2,2-Te~rachloroethana
Tetrachloroethena
[; Toluene
l,2-tran.-D1chloroe~hylene
l,l,l-Tr1chloroe~h&ne
Trichloroethene
Tr1ch1orofluorocc~hane
Vinyl chlor1de
Acatone 11. '. 101 111 211 14.1 600 B
2-Butanone --
Vinyl acetate
2-Sexanone
4-Hethyl-2-pentanone
Styrene
Total xylene.
r Concen~ratlon. le.. ~h.a.n the con~ract required detection l~lt..
B,SL Detected 1n realent blank,
J Laboratory e.~L=ated value. but could no~ be quantifled.
. Laboratory duplicate analy.l..
BSL Sazardou. Substance Lis~.
S Ou~.lde laboratory callbra~lon ranae.
-------
r.
cP
L
r
,<
- - .
1
J
-r
r
1"
Summary of Vola~~le Ora~~1c Compour.d Concentrat10ns Detected above the Contract Required
Detec~ion ~u:1t 1~ 50i~ 5L~les i~ :~. V1c1~ity of t~e 5Y-1C Area. Co"lected April 1988.
33C1 Edmunds 5~r..t 51te, AlbuGuerG~e, Ne~ Mexico.
lorLna Desianation:
Sample Inurval:
Dau Sampled:
Work Order Number:
Uni ta:
ISL
--------Replicate---------
SV10-5 SV10-5* SY10-5 SV10-5 SV10-5 SV10-5
5 - 7' 5 - 7' 10 - 12' 20 - 22' 30 - 32' 40 - 42'
4/12 4/12 ./12 '/12 ./12 '/12
P8-04-024 PI-04-024 P8-04-024 P8-04-024 P8-04-024 P8-04-024
(\&&/q) (\&&/q) (\&&/kl) (\&&/kl) (\&&/q) (\&&/kl)
18_8M
bia(ChlorQD8thyl)8~8r
Ir_form
Carbon t8trachloride
Chloroben.ene
Chlorodibromomethane
Cblo roe thane
2-Cbloroetbylvinyl ether
Chloroform
D1chlorobromomethane
l.l-Dichloroethane
1.2-Dichloroethane
trana-l.2-Dichloroethene
1.1-DLchloro.th.n.
1.2-Dichloropropane
cia-l.3-Dichloropropylena
Ethylbenaene
Kethyl bromide
Keth,l chloride
Kethylene chloride
1.1.2.2-Tetrachloroethane
Tetrachloroethene
Toluene
1.2-trana-D1chloroethylene
l.l.l-Trichloroethane
Trichloroethene
Trichloro!luoromethane
Vin,.l chloride
Acetone
2-lutanone
Vin,l acetate
2-Sexanone
4-Kethyl-2-pentanone
Styrene
Total xylenea
--
llJ
llJ
I.IL
J
Concentrations-less'than the contract required.detection 1Lmits.
Detected in reaaent blank,
Laboretory est~ted value, but could not be quantified.
Laboratory duplicate analysis.
Hazardous Substance List.
*
H5L
S
ua'a.a
Outside laboratory calibration ranae,
-------
~
[
~ r
I
~
-
I
~
.F
1.
r
t
.
Summary of Volatile Orlanic Compound Concentratio~ Detected above the Contract Required
Detection L~it 1~ Sc1l S~:e. in the Vicinity of the SV-10 Area, Collected April 1988,
3301 Edmun,b Street Site, Albuquerque, Ne" He..ico.
lor1n& C.ailnation:
Sample Inurval:
Dau Sampled:
Work Order IlulDber:
Unit.:
BSL
ieftaene
b1a(Chlor088~yl)etber
Ir_fon
Carbon ~etr.eblor1de
Cblorobenaene
Cbl orocl ibrD88088 thane
CbloroeUiaAe
2-Chloroethylv1nyl ether
Cblorofona
DlchlorobrDmam8thane
l,l-Dlchloroethane
1.2-D1chloroeth&ne
trana-l.2-Dlchloroethene
l,l-Dichloroethene
l,2-Dlchloropropane
c1a~l,3-Dlchloropropylene
Ethylbenune
Methyl brom1de
Meth,.l chloride
Methylene chlorlde
1.l,2.2-tetrachloroethane
tetrachloroethene
toluene
l,2-tran.-Dlchloroeth,.lene
l,l.l-trlchloroethane
trlchloroethene
trlchlorofluoromethane
Vin,l chloride -
Ace tone
2-lIutanone
VLnyl acetate
2-BeJlanone
4-Keth,.1-2-pentanone
St,.rene
Tota~ X'J'lenu
SV10-~
~O - ~2'
4/12
PI-04-024
(ua/q)
SV10-~
60 - 62'
4/12
'8-04-024
(ua/q)
SV10-~
70 - 72'
4/12
PI-04-024
(ua/q)
SV10-~
80 - 82'
4/12
PI-04-024
(ua/q)
SV10-~
90 - 92'
4/12
PI-04-024
(ua/q)
SV10-~
100 - 102'
4/12
'8-04-024
(ua/q)
14
~6
22
Concentratlons 1e.. than the contract required detectlonl~rmlts.
Detected in rea.ent blank.
Laboratory e.t~ted value, but could not be quantified.
Laboratory duplicate anal,..i..
Bazardou. Sub.tance Li.t,
II ,ilL
J
.
BSL
5
ul/kl
Out.ide laboratory calibration r&n&e.
-------
~~
~
~
~
"
I
I
r ,
i
5~ry of Vo~a~ile Orlanic Compound Concen~ra~ion. De~ec~ed
Oe~ec~ion Li=lt i~ Soil S~le. in the Vicinity of the SV-10
3301 t~d. Stree: Site. Albu~er~~e, Mev He..ico.
above ~he Con~ract Required
Area, Co~lectec April 1988.
lIorlna De.ilnAtion:
S&lllple Iatarval:
Dau Sampled:
Work Order NYmber:
Uait.:
BSL
--------aeplicate---------
SViO-6 SV10-6*
S - 7' S - 7'
4/12
P8-04-024
(uaf!ta>
4/12
P8-04-024
(ua f!ta >
SV10-6 SV10-6 SV10-6 SViO-6
10 - 12' 20 - 22' 30 - 32' 40 - 42'
4/12 4/12 4/12 4/12
'8-04-024 P8-04-024 P8-04-024 P8-04-024
(ua/!ta) (ua/q) (ulf!ta) (uaf!ta>
lenaane
bi.(Chloromethyl)etbar
Ir-form
Carbon tetrachloride
Chlorobaa.ene
Chlorodibroeometbane
Chlor08~hane
2-ChloroethylV1ny1 e~har
Chloroform
Dlchlorobroeometb&ne
l,1-Dichloroetb&ne
1,2-Dichloroetb&ne
tran.-l,2-Dlchloro8then8
1.1-Dlchloroethene
1.2-0ichloropropane
ci.-l.3-0ichloropropylene
Ethylben.ene
Kethyl brOCDide
Hethyl chloride
Hethylene chloride
l,1,2.2-Te~rachloroetbane
Te~rachloro.thene
Toluene
1.2-tran.-Oichloroethylene
l.l,l-Trichloroethane
Trichloroethene
Trichlorofluoromethane
Vinyl chloride
Acetone
2-lIutanone
Vinyl acetate
2-Be.anone
4-Hethyl-2-pentanone
Styrene
Total.xylene.
13
10 J
12J
12J
..-.----
II. ilL
J
Conc.n~ra~ion. le.. than ~he contract required de~ection llmit..
Detected in realent blank.
Laboratory e.t~ted value, but could not be quantified.
Laboratory duplicate analy.i..
Ba.ardou. Sub.tance Li.t.
*
BSt
5
ulfkl
Out. ide laboratory calibration rance.
-------
l
r
~ r
[
l
.
\.
r
1
.
I
1
Summary of Volatlle OrlL~ic C~o~~d Concentratlon$ Detected
Oetactlon Ll=it 1~ So1: S..~:e. in the Vlcl~ity o! the SV-l:
33C1 E~~ds Straa: Site, A:b'Jquarque, Ne... Mexlco.
abova the Contract Raqulrad
Area, Co:lactad April 1988.
lor1a& Des1lnation:
Sample Inurval:
Dau Sampled:
Work Order Number:
Unit.:
ISL
leD88ft8
b18(Cblor088thyl)ether
Ir_foC8
Carbon tetrachloride
Chlorobenaene
Chlorodlbramam8thaDe
ChloroethaDe
2-Chlor08thyl.1Dyl etnar
ChlorofoE1ll
D1chlorobromomethane
1.1-Dlchloroethane
1.2-Dlchloroethane
. tran.-l.2-D1chloroethene
1.1-D1chloroethene
1.2-Dlchloropropane
c1.-1.3-D1chloropropylane
Ethylbenaena
Mathyl tirOlDlde
Hathyl chloride
Mathylene chloride
1.1.2.2-Tetrachloroethane
Tetrachloroethene
Toluene
1.' --ans-Dlchloroathylene
1.1.1-Trlchloroethana
Trlchloroethane
Trichlorofluoromethane
Vlnyl chloride
Acetone
2-lutanone
Vinyl acetata
2-Beaanone
4-Hethyl-2-pentanona
Styrene
Total xylena.
SV10-6
~o - ~2'
4/12
'8-04-024
(ua/q>
SV10-6
60 - 62'
4/12
PI-04-024
(Ul/kl>
SV10-6
70 - 72'
4/12
PI-04-02'
(ua/q>
SV10-6
80 - 82'
4/12
'1-04-02'
(ua/q)
SVl0-6
90 - 92'
"12
PI-O'-024
(ua/q)
.
SV10-6
100 - 102'
4/12
'1-04-024
(ua/kl>
I.IL
J
Concentration. less than the contract requ1rad detect10n lim1ts.
Detected ln realent blank.
Laboratory astLm&ted valua. but could not be quant1f1ed.
Laboratory dupllcata analysls.
Bazardous Substance Llst.
.
BSt
S
ul/kl
Outslde laboratory callbratlon ranae.
-------
~
r
i.
. r-
~
.1
~
L
.r
I
. -1
1-
r'
1
Summary of Volat~:e Orlanic Compound Concentratlon. Detected
Detectlon Ll=lt ln Soil S~le. ln the Vlclnlty of the SV-10
3301 Edmund. Street Slte, Albuquerque, New Hexlco.
above the Contract Requlred
Area, Collected Aprl1 1988,
aorlna De.l'n&tlon:
Sample Inurval:
Date Sampled:
Work Order _umber:
0111 ta :
ISL
"_eM
~laCehlor088tb11>eth8r
Ir-foll:8
Carbon tetrachlorlde
Chlorobe_eM
Chlorodlbromamethane
ehlor-thane
2-ChloroetbylyLnyl ether
ehlorofore
Dlchlorobromometb&ne
l.l-Dlchloroethane
l,2-Dlchloroethane
trana-l,2-Dtehloroethene
1.1-Dlchloroethene
1.2-D~chloropropane
el.-1.3-Dlchlo.ropropyLene
!thylbenune
Kethyl br_lde
Kethyl chlorlde
Kethylene chlorlde
1.1.2,2-Tetrachloroethane
Tetrachloroethene
Toluene
1.~-tran.-D1chloroethylene
l,l.l-Trlchloroethane
Trlchloroethene
Tr1chlorofluor~thane
Vlnyl chlorlde
Acetone
2-!utanone
Vlnyl acetate
2-Be.anone
4-Hethyl-2-pentanone
Styrene
Total xylenea
--------Repllcate---------
SV10-7 SV10-7e SVl0-7 SV10-7 SV10-7 SV10-7
5 - 7' 5 - 7' 10 - 12' 20 - 22' 30 - 32' 40 - 42'
.,13 4113 4/13 4/13 .,13 .'13
'8-0.-025 "-0.-025 "-04-025 '8-04-025 PI-04-025 PI-04-025
Cualq> Cualq> Cualq> (ua/q> (ua/q> Cua/kl)
. "__0_...
Concantratlons les. than the contract requlred detectlon lLmlt..
Detected 1n realent blank.
Laboratory e.tL=ated value. but could not be quantlfled.
Laboratory dupl1cate analysls.
Barardoul Substance Llst.
Outslde laboratory callbratlon ranae.
Hlcrolr&C1 per kl1olrAm.
B,n
J
.
BSL
S
-------
t
[
~r
G
r -
L
I
I.
[
L
L
~
~
SummAry of Volati:e Orlanic Compound Concentration. Detected above the Contract Required
Detection L~it i~ Soil S~les in the Vlclnity of the SV-10 Area, Collected April 1988.
3301 E4mund. Street Slte. Alb~querque. New Mexlco.
lorina De.ilnAtion:
S8IIIple Inurval:
Dau S8IIIpled:
Work Order Number:
Uni~a:
!St
Ie_e-
bi.CCblor088~yl)e~er
I~foftl
Carbon ~e~r.chlorlde
Cblorobe_ene
Cblorodlbr_~haAe
Cbloroe~haAe
2-Cblor08thylyLDyl e~er
Chlorofonl
Dichlorobromomethane
l.l-Dichloroethane
1.2-Dichloroetbane
tr~-1.2-Dlchloroe~hene
l.l-Dichloroethene
1.2-Dichloropropane
cia-l,)-Dichloropropylene
Ethylbenaene
Methyl brOlDide
Methyl chloride
Methylene chloride
1.1.2.2-Tetrachloroethane
Tetrachloroethene
Toluene
1.2-tran.-Dlchloroethylene
l.l,l-Trichloroethane
Trichloroethene
Trlchlorofluor~thane
Vinyl chloride
Ac.atone
%-Butanone
Vinyl acetate
2-Bexanone
4-Methyl-2-pentanone
Styrene
Total .,.lene.
SVI0-?
50 - 52'
10(13
PI-01o-025
Cue (Ita)
SVIO-?
60 - 62'
4/13
PI-01o-025
Cue/Ita)
SVI0-?
70 - 72'
4(13
PI-04-025
(ue/Ita)
SVIO-7
80 - 82'
10/13
P8-01o-025
Cue/Ita)
SV10-7
90 - 92'
10/13
PI-01o-025
(UI/Ita)
SVI0-?
100 - 102'
4/13
P8-01o-025
Cue(k,)
15
B,Bt
J
Concentration. le.. than the contract required detec~lon-lLmit..
Detected in realent blank.
Laboratory e.t~ted val~e, but could not be quantlfied.
L.boratory duplicate analy.l',
Ba&ardo~. Sub.tance List.
.
BSL
5
ug/kl
Outslde laboratory calibration range.
-------
r
r.
[
~r
[
,
J ..
r
i
f
r
t
S~ry of Vola~Lle Or.anlc Compound Concen~ratLons De~ec~ed
De~ec~Lon Ll=L~ Ln SoLl Samples Ln ~he VLcLnL~y of ~he 5V-10
33~1 Edmunds Street SL~e, Albu~~erGue, New HexLco.
above ~he Con~rac~ Requlred
Area, Collec~ed Aprll 1988,
lorlna De.l,na~lon:
Sample In~erval:
Dau Sampled:
Work Order lumber:
OnU. :
ISL
lcAaene
bl.(Chlor088~yl)e~her
Ir-forlll
Carbon ~e~r.chlorlde
ChlorobenaeM
Chlorodlbr-~hane
Ch10roe~hane
2-Cbloroe~h71Y1n71 e~her
Chloroforlll
Dlch1orobroeome~hane
1.1-Dlchloroe~hane
l,2-Dlcbloroe~hane
tran.-l.2-DLchloroethene
1.1-Dlchloroe~hene
1.2-Dlchloropropane
cl.-1,3-DlchloroproP71ene
E~hylben.ene
Ke~hyl br-lde
"'~hyl chlorlde
Methylene ch10rlde
l,l.2.2-Tetrachloroethane
Tetrachloroe~heD8
TolueM
1.2-trans-Dlchloroethy1ene
l,l.1-Trlchloroethane
TrLchloroethene
Tr1chlorofluoromethane
Vlnyl chlorlde
Acetone
2-Butanone
Vlnyl ace~ate
2-Bexanone
'-Heth7l-Z-pentanone
Stynne
Totd zylene.
--------Repllcate---------
SV10-a SVl0-a* SV10-a SV10-8 SV10-8 SV10-8
5 - 7' 5 - 7' 10 - 1Z' ZO - 22' 30 - 32' '0 - 42'
4113 4113 4/13 4/13 "13 "13
PI-04-025 PI-04-025 P8-04-0Z5 pa-04-025 P8-04-015 P8-04-025
(ua/ka) (ua/ka> (ua/ka> (ualka) (ualka> (ua/k,)
.
--
-. -.--. ..
B,U
J
Concentratlon. 1e.s ~han the contrac~ requlred de~ec~lon 1Lml~..
'-..... '
could not be quantlf1ed.
De~ected in rea.ent blank.
Laboratory estL=&~ed value, but
Laboratory dupllcate ana17s1s.
Bazardous Substance Llst.
Outslde labor&tor7 calLbra~1on r&nal.
Hlcrolrams per kl10IrL~.
*
BSL
S
-------
,
L
I
l
f
l
1
f
t
Summary of Vola~ll. OrlL~lc Compoun~ Conc.n~ra~lon. Detec~ad above ~he Con~ract Requlr.~
De~.c~lon Ll=l~ in Soll S~l.. in ~~e Vlclnlty of ~he SV-10 Area, Collec~e~ Ap~ll 1988.
330: Edmun~. S~ree: Sl:e. A:buquerque. New Mexlco.
lor1D& De.llnatlon:
Sample Interval:
Dau Sampled:
Work Order IYmber:
Un1t.:
SV10-8
60 - 6Z'
4/13
P8-04-0Z.5
mo-,
70 - 7Z'
4/13
P8-04-0Z.5
(ua/kl)
SV10-8
10 - 8Z'
4/13
PI-04-0Z.5
(ua/Ita)
SV10-8
90 - 9Z'
4/13
PS-04-0Z.5
(ul/kl)
SV10-8
100 - 10Z'
4/13
P8-04-0Z.5
(ua/kl)
SV10-8
.50 - .5Z'
4/13
P8-04-0Z.5
(ua/kl)
(ua/lta)
1St
"neene
bl.(Chlor088thyl)etbar
Ir_lorID
Carbon t.trachlorlde
Chlorobena.ne
Chlorodibroeametb&n.
Chloroethan.
Z-Chloroethyl.1nyl eth.r
ChloroforID
Dichlorobromomethane
l,l-Dichloroethane
1.Z-Dlchloroethan.
tran.-l,2-Dichloroethene
l.l-Dlchloroethen.
1.Z-Dlchloropropane
Cl.-1,3-DiChloropropYle~.
Ethylbenaene
Kethyl br_lde
Methyl chloride
Methylene chlorlde
1.l,2.Z-T.trachloroethan.
Tetrachloroethene
Tolu.n.
1.Z-tran.-Dlchloro.thylen.
l.l.l-Trlchloroethane
Trlchloroeth.ne
Trlchlorofluor-.thane
Vinyl chloride
Acnone
Z-lIu~anone
Vinyl acetate
Z-Bexanone
4-Hethyl-2-pentanon.
Styrene
Total xylene.
II. ilL
J
Concentratlolu. le.. than the con~ract required detection limit.
Oetected ln realent blank.
tabora~ory e.tLmated value. but could not be quantifi.d.
taboratory duplicate analy.l..
Razardou. Sub.tance tl.~.
.
BSL
S
ul/kl
Out.lde laboratory calibratlon ranae.
-------
.
C(
r
I..
r
l
,L
I
[
~
1.
L-
r
i
y-
o
1
t
Summary of Volati:e OrlL~ic Compound Concentration. Detected
Detection Ll=it L~ Soil S~les in the Vicinity of the SV-l0
3301 Edmund. Street Site, Albuquerque. New Mexico.
above ~e Contract aequired
Area, Collected April 1988,
lorlne De.llnation:
Sample Inurval:
Dau 5ampled:
Work Order lumber:
UDlta:
ISL
leD&e-
bla(Chlor088thyl)etber
Ir-fonl
CarboD tetrachlorlde
Cbloroben.e-
Chlorodlbromometbane
Chlor-tbane
2-Chlor_thylvlnyl ether
Chloroform
Dlchlorobromomethane
l.l-Dichloroethane
1.2-DLchloroethane
trans-l.2-Dlehloroethene
l.l-Dlchloroethene
1.2-DLchloropropan.
Cl.-1.3-Dlchloropropylene
Ethy 1 benaene
Kath,.l br_ide
Kath,.l chloride
Kethylene chloride
1.1.2.2-Tetrachloroethane
Tetrachloroethane
Toluene
1.2-tr~-Dichloroeth1lene
1. 1. I-Trichloroethane
Trichloroethene
Trichlorofluoromethane
Vlnyl chlorlde
Acetone
2-lIutanone
Vin,.l acetate
2-Be"anone
4-Meth,.l-2-pentanone
Styrene
Total .,.lane.
$VI0-'
5 - 7'
4/14
58-04-082
(ua/ka)
--------.epllcate---------
$VI0-' $VI0-'. $VI0-' $Vl0-' SVI0-9
10 - 12' 10 - 12' 20 - 22' 30 - 32' 40 - 42'
4/14 4/14 4/14 4/14 4/14
58-04-082 58-04-082 58-04-082 58-04-082 58-04-082
(ua/ka) (ua/ka) (ua/ka) (ua/ka) (ua/ka)
121
131
II.IL
J
Concentration. le.. than the contract required detection lLmlt.
Detected in realent blank.
Laboratory est1m&ted value. but could not be quantified.
Laboratory duplLcate anal,.sL..
Bazardous Substance Ll.t.
Outside laboratory calibration ranle.
Microlrams per kilolram.
.
aSL
S
-------
'.1-
-
!""
...
~
1
[
r.
L
l
\
~
1
Summary of Vola~l:e OrlL~le Compound Coneentrat1on. De~ee~ed
o.~ec~lon L~1t 1n So~l S~le. 1n the V1einity of ~he SV-10
3301 Edmund. Street Site. Albuquerque. Nev Mexieo.
above ~he Con~rae~ Requlred
Area. Collec~ed April 1988.
lor1na o.allnaUcm: . SV10-9 SV10-9 SV10-9 SV10-9 SV10-9 5V10-9
Sample In~erva:: 50 - 52' 60 - 62' 70 - 72' 10 - 12' 90 - 92' 100 - 102'
Date Sampled: 4/110 4/14 4/14 4/110 4/110 4/110
Work Orde r .\Dbe r: 58-04-082 58-04-082 58-04-082 58-04-082 58-04-082 58-04-082
OnU.: (\/.I/q) (\/.I/q) (\/.I/q) (\/.I/q) (\/.I/kl) (\/.I/kl)
ISL
~ene
~ia(Cblora88th71)e~bar
Ir-fom
CarboD ~atl'achloride
Cblorobenaana
Chlorodibr08088thane
Chlor"~hana
2-ChloroathylY1ft71 a~h8r
Chlorofol"lD
Dichlorobramamethane
1.1-Dlch!or08~hane
1.2-Dlchloroethane
tr&nA-1,2-Dichloroe~hene
l,l-D1chloroe~hene
1.2-Dlchloropropane
cl.-1.3-D1chloropropylene
Ethylbenaene
Methyl br_lda
Methyl chloride
Methylene chloride
1.l,2,2-Te~rachloroethana
Tetrachloroethane
Toluene
1.2-tran.-Dlchloroeth71ene
1. 1 ,l-Trlchloroethane
Trichloroethene
Trlchlorofluoro=c~h&ne
Vinyl chloride
Acetclfte
1'1
131
121
121
131
. - _0- _. _.
2-Butanone
Vinyl acetate
2-Bexanone
4-Kethyl-2-pentanone
Styrena
Total xylene.
I.IL
J
Concen~ratlona le.. ~han the con~rac~ requlred detec~lo.~ llmi~.
De~ec~ed 1ft realen~ blank.
L.bora~ory e.~LmAted value, but could not be quantlfiad.
Laboratory dupllca~e analy.l..
Bazardoua Sub.tance Llat.
.
BSL
5
ul/l<.&
Outalde laboratory callbratlon ranae.
-------
~
..,
~ .
~
c
r
I
r
r
,
r
Summary of Vola~ila Orlanic Compound Concan~ra~ion$ Da~ac~ed
De~ec~ion LL=i~ i~ 50il 5&:plas in ~he Vicini~y of ~he SV-1C
3301 Edmund. S~reet Si~e. Albuquerque. Nev Mexico.
above ~he Con~rac~ Re~uired
Area, Collec~ed April 1988.
--------Repllcate---------
Ior1na De.lanatlon: SV10-10 SV10-10 SVl0-l0. SV10-l0 SV10-10 SVl0-l0
Sample Inurval: , - 7' 10 - 12' 10 - 12' 20 - 22' 30 - 32' 40 - 42'
Dau Sampled: 4/14 4/14 4/110 4/14 4/14 4/14
Work Order lIwDber: 58-04-092 58-04-092 58-04-092 58-04-092 58-04-092 58-04-092
Urd.u: (ua/q) (ua/q) (ua/q) (ua/q) (ua/q) (ua/q)
ISL
leuena
bla(Chlor088thyl)ether
Ir-fo-
Carboft tetrachloride
Chlorobenaene
Chlorodibr_U\ane
Chl oroe thane
2-ChloroethrlYlDrl ather
Chlorofo-
Dleh1orobromamath&n8
l,l-Dlchloroethane
l,2-DLchloroethane
trana-l.2-DLchloroethene
l.l-Dichloroethene
1.2-Dlchloropropana
cla-l.3-Dlchloroproprlana
Ethrl benaane
Kathrl br-Lde
"ethyl chlorlde
Kathrlene chloride
l,l.2,2-Tetrachloroethane
Tetrachloroethene
Toluene
l,2-tran.-DLchloroethrlene
l.l.l-Trichloroethane
Trichloroethane
Trlchlorofluorome~hane
Vlnrl chlorLde
Acetone .- UI . -- - 101 121 141
2-lutanone
VLnrl acetate
2-Se.an.one
4-Kethrl-2-pentanone
Strune
TotaL: xylene.
II,U
J
Concentratlon. le.. than the contract required detectlon 11mlt.
Detected ln realent blank.
.
Laboratory e.t~ted value, but could not be quantifLed.
Laboratory duplica~e &naly.ls.
Sazardou. Substance Li8t.
Outside laboratory calibration ranee.
Mlcrolram. per kl10lram.
SSL
5
-------
-
.
l
r
G
L
I
I:
f
L
r
('
- t-
Summary of Vola~1le Or1L~1c Compound Concen~rat1on. Detected
De~ect1on L~1~ 1n S011 Samples 1n the V~c1nit' of ~he SV-1:
3301 Edmund. S~reet S1te. Albuquerque. Mev Mex1co.
above ~he Con~rac~ Required
Are.. Collected April 1988.
lorlac DeailD&~ion:
Sample Inurval:
Dau Sampled:
Work Order Ju8ber:
Uni~a:
1ISL
---eZUI
~i.(Cblor088th1l)e~r
Ir_form
Carbon ~e~rach1orid.
CblorobeGa.-
CblorocHbr-~baA.
QUoro.~han.
2-Chlor08~b,lvin7l .~b8r
Chloroform
Dicblorobr0mam8~han.
l,l-Dichlor08~e
l,2-Dichlor08~ban.
~r&n8-1,2-Dichloro.~hene
l,l-Dlchloroe~hene
l,2-D1chloropropane
cla-1,3-D1chloropropyl.ne
E~hylben..ne
K.~h7l br_1d.
Ke~hyl chlodd.
Ke~hylen. chlorld.
l,l,2,2-T.~rachloroe~han.
T.~rachloroe~bene
Toluene
l,2-~ran.-D1chloro.~hylen.
l,l,l-Trlchloroe~hane
Tr1chloro.~hene
Tr1chlorofluor~~hane
Vinyl chloride
.Acetone
Z-!lu~anone
Vinyl ac.ta~.
Z-Sexanon.
4-Ke~hyl-Z-pen~anone
S~,rene
Toul .,.18n..
SV10-10 SV10-10 SV10-10 SV10-10 SV10-10 SV10-10
50 - 52' 60 - 6Z' 70 - 72' 80 - 82' 90 - 92' 100 - 102'
4/14 4/14 4/14 4/14 4/14 4/14
'1-04-092 SI-04-092 SI-04-092 $1-04-092 S8-04-092 58-010-092
(ua/ka) (ua/ka) (ua/ka) (ua/lLa) (ua/k,) (ua/k,)
1.3 I
5.3 I
3,30015
4'0 S
I,lL
J
Concen~ra~1on. le.. ~han ~he contract required detec~ion l~it.
Detected 1n realent blank.
Laboratory e.~L=a~.d value, bu~ could not be quantified.
Labora~ory dup11ca~e analy.1..
Sazardou. Sub.~anc. Li.~.
.
BSL
S
u,' ILa
0u~.1d. labora~ory ca11bra~1on ranae.
-------
k;
r-
l
r
L.
.- f
j
l
r
1
Summary of VolatLle Orl~~Lc Compound ConcentratLon. Detected
DetectLon LW:Lt Ln Soil S~le. in the Vicin"t, of the SV-1C
3301 Edmund. Street SLte. Albuquerque, "ev He.Lco.
above the Contract Required
Area, Collected April 1988.
lorlna Deallnatlon:
SUlClh Iaurval:
Dau 5ampled:
Work Order .umber:
ODlta:
5ViO-U
. ~ - 7'
4/15
58-04-092
--------Repllcate---------
SV10-U SViO-U- SViO-ll SViO-ll SViO-U
10 - 12' 10 - 12' 20 - 22' 30 - 32' 40 - 42'
4/15 4115 . "15 4/15 4/15
58-0'-092 58-04-092 58-04-092 58-04-092 58-04-092
(ua/lta) (ua/lta) (ua/q) (ua/q) (ua/lta)
(ua/kl)
ISL
"Daene
bla(Chloromath,l)ether
Ir_foRl
Carboa tetrachlorlde
Cb1orobenaene
Cblorodlbromomathane
Chloroethane
2-Chloroeth,lvin,l ether
ChlorofoRl
Dichlorobromomathane
1.1-Dlch1oroethane
1.2-Dichloroethane
trana-1,2-Dichloroethene
1.1-Dichloroethene
l,2-Dichloropropane
cia-1,3-Dichloroprop,lene
Zth,lbenune
Meth,l.bc_lde
Meth,l chloride
Keth,lene chloride
l,l,Z,2-Tetrachloroethane
Tetrachloroethene
Tolu.n.
5.71
1.Z-trana-Dichloroeth,l.ne
1.1.l-Trichloro.thane
Trichloroethene
Trichlorofluoromethane
Vln,l chlorlde
Aceton.
2-lutanone
Vin,l acetate
Z-Se.anona
-
4-Hethyl-2-pentanone
5t,rene
Total .,lene.
... .---.--
I,ll.
J
Concentrationa 1e.. than the contract required detection limlt.
Detected ln realent blank.
could not be quantified.
.
Laboratory e.t~ted value, but
Laboratory duplicate anal,. 1..
la&ardoua Sub.tance Llat.
Out.ide laboratory calibration canae.
S5L
5
ul/kl
-------
Summ&~ of Volatile Orlanic Compound Concentrations Oetected
Oetection LL=it in Soil S~les in the Vicinity of the SV-10
3301 Edmund. Street Site, Albuquerque, Hew Mexico.
above the Contract Required
Area, Collected A?ril 1988,
10r1n& Desilnation:
Sample Inurval:
Date Sampled:
Work Order Number:
Units:
ISL
SV10-11
50 - 52'
'/15
51-0'-092
(UI/Ita>
SV10-11
60 - 62'
'/15
58-0'-092
(UI/Ita>
SVl0-11
70 - 72'
'/15
51-0'-092
(UI/Ita>
SVl0-11 SVl0-11 SVl0-11
10 - 12' 90 - 92' 100 - 102'
'/15 4/15 '/15
58-0'-092 58-04-092 S8-0'-092
(ua/Ita> (UI/kl> (UI/Ita)
"_eae
~Ls(Cblor088~yl)ether
Ir_fonl
Carboa tetrachloride
CbloroMnaene
.-.
Chl orod i br08088 thane
Chloroethane
2-Chloroethylvin,1 ether
Chloroform
Dichlorobromomethane
1.1-Dichloroethane
1.2-Dichloroethane
trans-l.2-Dichloroethene
l,l-Dichloroethene
1.2-Dichloropropane
cia-l.3-Dichloroprop,lene
Ethylbenune
Methyl bromide
Methyl chloride
Methylene chloride
1.1,2,2-Tetrachloroethane
Tetrachloroethene
.
r
Toluene
1.2-trana-Dichloroeth,lene
1.1.1-Trichloroethane
Trichloroethene
Trichlorofluor~thane
Vinyl chloride
Acetone.
f
,
- - _. _. -
2-Butanone
Vinyl acetate
2-BeJianone
'-Methyl-2-pentanone
Styrene
Total JI"11enu
111
5.1 I
220 I
;
I,ll
J
Concentrations less than the contract required detection ~~i~.
Detected in realent blank.
Laborator, estL=ated value, but could not be quantified.
.
BSL
S
u.'k.
Laborato~ duplicate anal,sis.
Ba&ardous Substance Li.t.
Outside laborato~ calibration ranae.
-------
L
k
r
,"
\.
I
[
t
1
..
\
"
Summary of Volat11e Orlan1c Compound Concentrat10ns Detected
Detect10n ~l=1t 1~ Soil SAMPles in the VicLnity of the SV-10
33C1 Edmunds Street S1te, Albuq\.Iuque, New HuLco..
above the Contract Req\.lLred
Area, Collected April 1988,
lor1Da De811AatlOD:
Saqlh Inurval:
Deu 5ampled:
Work Orde~ IU8bar:
Un1ts:
ISL
SV10-11
110 - 112'
4/15
5'-04-092
(ua/kl)
lenaene
~18(ChlorG88tbyl)etba~
Ir_foEa
Carbon CeC~achlO~1de
Chlorobenae-
Chlorod1br08088~e
Chloroethane
2-ChloroethylvLnyl ether
Chloroform
D1chlorobromaa.tbane
l,l-Dichloroethane
l,2-Dichloroethane
tran.-l.Z-Dlcbloroethene
l,l-Dlchloroethene
l,2-Dichloropropane
cis-1.3-Dichloroprop,lene
I:th,lbenaane
Hath,l br_ide
Hath,l chloride
Meth,lene chloride
1.l,Z.2-Tetr8chloroethane
Tetrachloroethene
Toluene
1.2-trans-Dichloroetbylene
1. 1. 1-Trlchloroethane
Trlchloroethene
TrLchloro!luoromethAne
VLn,l chlorlde
Acetone
2-Butanone
Vln,l acetate
2-Beaanone
4-Meth,1-2-pentanone
St,rene
Total .,lene.
7.!l1
11
111
B,IL
J
Concentrat1on. le.. than the contract requLred detection 11m1t.
Detected 1n realent blank.
.
Laboratory e.tLmated value, but could not be quantif1ed.
Laboratory duplicate anal,.1s.
Bazardou. Sub.tance Li.t.
BSI.
S
ua/kl
Out.Lde laboratory calibrat10n renae.
MLcroarAm. per kLloaram.
-------
[
~,-.
t.:
...
- -
~
r
t
r
t
Summary of Vo1a~~le Or&&r.lc Compound Concen~ra~lo~. Detec~ed above ~he
De~ec~1on L~l~ in Soil S~le. in ~he Tank Farm Area. Col1ac~ad April
S~reet Site, AlbuGuerque. New Mexico.
Sample I. D. :
Sample Inurval:
Dan Sampled:
Work Order Numbar:
Unit. :
TFNE C')
, - 7'
4/6
58-04-024
\illkl
TFItE (10)
10 - 12'
4/6
58-04-024
\i1/1L1
TFIfE (20)
20 - 22'
4/6
58-04-024
\i1/1L1
B5L
lanaana
bi.CChlor088thyl)ether
Ir-fonl
Carbon cecrachlorida
Chloroben.ane
Chlorodibromomethane
Chloroethana
2-Chloroathylvin,1 athar
Chloroform
~ichlorobromomethana
1.1-Dichloroathana
1.2-Dichloroathana
tran.-l,2-Dichloroathena
1.1-Dichloroathene
1.2-Dlchloropropane
ci.-1.3-Dlchloropropy1ane
E~hylbanlene
Hethyl brOlDlda
Me~hyl chlorida
Methylana chlorida
1.1.2.2-Tatrachloroethane
Tetrachloroathana
110
21
Toluena
1.2-tran.-Dlchloroathylane
l,l.l-Trlchloroetbane
Trichloroethane
Trlchlorofluorom.~hane
8.7
VInyl chloride
Acetone
1711.
1911.
18 11.
2-Butanone
VInyl acet.ta
Z-Se.anona
4-Methyl-2-pantanone
S~yrane
To~.l JlYlene.
TFMWC'J
, - 7'
4/6
58-04-024
u.a/1L1
Contrac~ Req~lred
1988, 3301 Edmund.
---------Repl1ca~e---------
TFMW (0)
10 - 12'
4/6
58-04-024
\i1/1L1
--
19 11.
TFIN (0) .
10 - 12'
4/6
58-04-024
u.a/k&
v
--
14
iliL
20 B1.
B.BL
J
Concentration. le.. than ~he con~ract required detection l~1t..
De~ected in realen~ blank.
Labora~ory e.t~ted value. but could not be quantIfied.
Labora~ory dupllca~e .ample.
N.E. Tank Farm Are..
N.W. Tank Farm Are..
.
UltE
TFIN
BS:"
u&/k&
Bazardou. Sub.tanc. List.
-------
Summary of Vola~lle Orlanlc Compound Concen~ra~lon. De~ec~ed above ~he Con~rac~ Required
De~ec~lon L~~~ in Soil S~les in ~he Tank Farm Area, Collec~.d April 1988, 3301 Edmunds
r
~,\;
S~ree~ sae, Albuquerque, Nev Mexlco.
SUlple I.D.: rnm (~) rnm (10) rnm (15) TFMD (20) rrSW (~) TFSW (10)
5ample Inurval: ~ - 7' 10 - 12' 1~ - 17' 20 - 22' ~ - 7' 10 - 12'
Dau 5&m;1led: 4/6 4/6 4/6 4/6 4/6 4/6
Work Order Number: 58-04-024 S8-04-024 58-04-024 58-04-024 58-04-024 58-04-024
UI11~s: ua/ka ua/ka ua/ka ua/ka \ll/ltl \l1/1t1
15L
lelUleca
~L.(Cb1or088ch,l)e~r
le-fon!
CaeboG ~.~racb1orLd.
Chloro~lUI.ne
CblorodLbrODOm8~hane
Chlor08~hane
2-Chloroe~hylvLnyl e~her
Chloroform
nicblorobromome~hane
l,l-Dichloroethane
l,2-Dlchloroe~hane
tean8-1.2-Dichloroethene
l,l-Dlchloroethene
l,2-Dichloropropane
cis-l,)-Dichloropropylene
Ethylben.ene
Kethyl br-ide
"eth,l chloride
"e~h,lene chloride
l,l.2,2-Te~rachloroethane
Tetrachloroe~hene
Toluene
l,2-tr&ns-Dichloro.~hylen.
1.1,l-Trlchloroe~hane
Trichloroe~hene
Trlchlorofluorome~hane
Vln,l chloride
Acetone 161L 13 IL 171L 211L 181L
2-lIu~anone
Vlnyl ace~ate
2-S..anone
4-Me~hyl-2-p.ntanon.
Styrene
Total Jr71enes
[
~r
u
~
f
. J
1
II ,ilL
J
TFSW
Tn![)
BSL
ul/kl
1
Concen~ration..les. ~han ~he contract required detection lLmits.
Detected in realent blank.
Laboratory est~t.d val\le, but could not b. quantified.
Labor.~ory duplica~e sample.
S.W. Tank Farm Area.
Mlddle Tank Farm Are..
Bacardou. Subs~ance Ll.~.
-------
..
Summary of Volatile Orlanic Compound Concentration. Detected above the Contract aequired
Detection LL=it 1n Soil Sample. In the Tank Farm Area, Collected Apr11 1988, 3301 Edmund.
Street Slte, Albuquerque, Nev He.lco.
,
I
---------aeplicate---------
SUlp1e I.D.: nSW (15) TFSW (ZO) TFSW (ZO) . nSE (5) nSE (10) TFSE (10)
Sample Inurval: 15 - 17' ZO - ZZ' ZO - ZZ' 5 - 7' 10 - 12' 15 - 17'
Date Sampled: 4/6 .,6 4/6 4/6 4/6 4/6
Work Order Nuaber: SI-04-0Z4 S8-04-0Z4 SI-04-0Z4 SI-04-0Z4 S8-04-0Z4 S8-04-0Z'
Unit.: \l.&/kl \l.&/ka \l.&/ka \l.&/ka \l.&/kl \1.& 1 kl
r
BSL
"naane
bia(Cblor088~,l)a~r
Jr_for8
CarboD cacracb10rLda
[
Chlorobanaane
ChlorodLbromomethana
[
Chloroethane
Z-Chloroath,lyLn,l ather
Chlorofonl
D1chlorobromomethane
l,l-DLchloroathane
l,Z-DLchloroethane
~
I
i.
crana-l.Z-Dlchloroethene
1.1-DLchloroethene
1.2-DLchloropropane
cL.-l.3-DLchloroprop,lene
Ethyl ben..ne
"eth,.l bromide
Ked~,.l chloride
"ethylene chloride
l,l.2,Z-Tetrachloroethane
Tetrachloroethene
Toluene
l,Z-tran.-DLchloroethylene
1,l,l-Trichloroethane
,.~. .
trichloroethene
Trichlorofluor~thane
--
L
V1n,l chio~ld.
Aceto..e
tilL
14 IL
18 IL
16 BL
l.
2-lutanon.
Vinyl acetace
.-
t.
2-ae.anone
4-Heth,.1-2-pentanone
Styrene
Total xylene.
I,lL
J
.
TFSW
tFS£
BSL
\l.&/ka
I
Concentrat10n. le.. than the contract requ1red detect10n lL=lt..
Detected 1n realent blank.
Laboratory e.t~ted
Laboratory dupl1cate
S.W. Tank Farm Area.
S.E. Tank Farm Area.
aazardou. Sub.tance L1.t.
value. but could not be quantified.
"nip le .
-------
Summary of Volatile O:aanlc Compound Concentrations De:ected above the Contract Required
Detection Li:~: in Soil Samples in the North &nd West Leachfield Areas, Collected
April 1988, 33Cl E~~ds 3tree: Site. Albuquerque, Nev Mexico.
~
Sample I.D.:
Sample Interval:
Dau Sampled:
Work Order lumber:
Units:
North L.r.
10 - 12'
4/5
58-04-026
ua I k&
North L.r. West L.r. West L.r.
20 - 22' 10 - 12' 20 - 22'
4/6 4/5 4/5
58-04-024 58-04-024 58-04-026
ua/ka ua/ka ua/ka
~
r
BSL
lensene
-r
bia(Chloromethyl)ether
I rOlllDf Onl
Carbon tetrachloride
r
M
Chlorobenaene
Chlorodibronomethane
Chloroethane
2-Chloroethylvinyl ether
Chloroform
Dichlorobromcmethane
l,l-Dichloroethane
1.2-Dichloroethane
trana-l.2-Dlchlorotthtne
'.
1.1-Dichloroethene
1.2-Dichloropropane
cis-l.3-Dichloropropylene
Ithylbenune
Methyl brOCllide
Kethyl chloride
Methylene chloride
1.1.2,2-Tetrachloroethane
Tetrachloroethene
Toluene
c
t:
1.2-trans-Dichloroethylene
1.1.1-Trichloroethane
Trichloroethene
Trichlorofluoromethane
Vinyl chloride
Acetone
118
2-But&l\one
Vinyl acetate
2-Hexanone
It-Methyl-2-pent&none
Styrene
Total xylenes
8,BL
BSL
111& I kl
Concentrations less than the contract required detection llmits.
Detected in realent blank.
Hazardous Substance List.
------- |