HomeMy WebLinkAboutWI0400023_Project Meeting_20010607Remediation of W.P. Ballard and
Surrounding Properties
Project Meeting
June 7, 2001
0
`'`e�igroup
Proposed Agenda
• Site Status Update
• Discuss Proposed Phase 3 Injection Plan for
Full Scale In Situ Chemical Oxidation
• Regulatory Approvals Status
0
`'1eqigroup
2
Corrective Action Objectives
• Achieve Site Specific Remedial Goals
• Achieve by September 2002
0
`''e�igroup
qo�v :;2M 5 �►a
3
Corrective Action Plan - Scope
• High Vacuum Dual Phase Extraction
• In Situ Oxidation with Permanganate
0
`lw�igroup
4
High Vacuum Dual Phase Extraction
• 29 Deep Dual Phase Extraction Wells
• 14 Shallow Soil Vapor Extraction Wells
• 9 air injection points
• Dual Objectives
address highest concentrations in source and
down gradient
— enhance permanganate application
0
`he0g'r-oup
Technology Overview - High Vacuum Dual
Phase Treatment
• De -water formation
• Remove adsorbed phase contaminants from
created vadose zone
• On -site treatment of soil vapor and
groundwater
• NPDES Discharge of treated water
• Permitted Discharge of treated air emissions
0
the �igroup.
s
6
High Vacuum Dual Phase System
• Wells installed Jan -
February 2000
• Trenching, Piping &
Vaults - March -April 2000
• Equipment - June - July
2000
• Final Install - Sept - Dec
2000
• Start-up - January 2001
`''e(49'r-oup
High Vacuum Dual Phase System
Water Treatment System
Thermal Oxidizer
`"e0group
High Vacuum Dual Phase System
High Vacuum Pump & Manifold
0
the
Ogro up.
SVE Pump & Air Supply Compressor
9
HVDP System Status
• January/February 2001 Completed System
Installation & Initial Testing
• March 2001 Groundwater and Soil Vapor
Extraction Systems Started
• June 2001 Proposed Start -Up of High
Vacuum Extraction System
0
`''eOgr-oup
10
Groundwater Extraction Results
• All 29 High Vacuum Extraction Wells Have
Been Operated and Developed
319,588 Gallons Recovered and Treated
• Mass Removal:
— 0.617 Ibs Trichloroethene
— 2.267 Ibs Tetrachloroethene
0
`he0group
Soil Vapor Extraction System Results
• System has operated approximately 800 33dQLj S
hours to date due to difficulties with
catalytic oxidizer
• Mass Removal:
— 2.26 Ibs cis- 1,2-Dichloroethene
— 1.69 Ibs Trichloroethene
— 132.98 lbs Tetrachloroethene
`heOgroup
12
In Situ Oxidation with Permanganate
• Geoprobe8 Application
• Zone Application Regime
• Bench tests used to determine site -specific
stoichiometric ratio
• Pilot test used to test injection method
• UIC permit application submitted May
1999; approved April 2001 for Phase 1 &2
`''Q(4group
13
(4.
MAPPING CWTWfl INTERVAL SHOMN HEREON = 2 FEET.
PROPERTY LINE FROM PLAN ENTITED-ALTA/ACSM LAND
PILE SURVEY FOR: CREENSBCRC D.C. PARTNERS. LTD.'.
DATED 1/11/95 PREPARED BY ROBERT E. WLSON. INC.
the Vf*oup
ZONE 1
40 GEOPROBE POINTS 10' R.O.I.
(ND) SET ON 20' CENTERS
(INU)
GRAPHIC SCALE
60 30 60 D
IN FEET )
I
LEGEND ____l
(313) TOTAL VOC CONCENTRATION
IND) NOT DETECTED I
—I(11J'--TOTAL VOC CONCENTRATION CONTOUR
® x axixc .Eu
n xElnEoxcEo concAErz rare /
® Sewes�nncN xan nrf III
c.s vu.E
9
14
M ®2
®,1
BUILDING
Z /
% BUILDING I I
Z II 1
BLOCK WL �
O SVMP
WITH STORAGE T NK ! ' -
x
— -,JMP,l
® POUE VM S P,
MW_4
—_ ®VMP,4
r�
SVMP_9
MW-ry W-2
M,N, 6
BUILDING
F`0 POtE
IG
DING \ \
VEMENT
i EDGE OF PP
LEGEND
Of PAVEMENT _—.-,'� - --
EpGE ���.. .�
P
GRAPHIC SCALE
to s to z6
® Ir � wuL
Sp
R
\ RCP
q
IN FEET)
NOTES:
HORIZONTAL DATUM IS NAD '83.
VERTICaE
DATUM IS NM'29,
THIS SA NOT A BOUNDARY SURVEY.
NOT FOR RECORDATION.
xEIxF a ax� %PE
p P
O® ss�wA¢ RxxHnE
n0u
DQ wArtx vu,2
( Ole nroxwlr
- \
MAPPING SCALE 1 INCH = 60 FEET.
MAPPING CONTOUR INTERVAL SHOWN HEREON = 2 FEET.
PROPERTY LINE FROM PLAN ENTITLED "ALTA/ACSM LAND
C Ensmc wax PAP[
® scw1R NxxxoU
T TIE SURVEY FOR: GREENSBORO D.C. PARTNERS, LTD.',
\
DATED 5/12/95 PREPARED BY ROBERT E. WILSON, INC.
D4 cxs vLLW
ZONE I : INJECTION POINT LAYOUT I
(20' CENTERS)
R' CGII NMI M
N011TN CAl10ARD EM4 MIC
Arr.faaa..r
i—a xc 21 R law) —2221
TEMPORARY INJECTION
POINT LAYOUT
ZONE I
W.P. —I-ARO PROPERTY
xNox GREENSBORO, NC
axO n: 9[t RHWrt: clRaao e..
vnne 3/2/99 Ac�o 15360A5E
III ��O)63S
8
the vf*oup- 15
1
Pilot Test
• 24 injection points
• 15% Sodium
Permanganate solution
• injected with
GeoprobeOO to 65' bgs
• April -May 2000
thev),group.
lyisurs ad Gnu
SslahNf WKWIJ
16
Pilot Test Chronology
• Baseline Sampling- March 21-24, 2000
• Phase 1 Application - April 25-May 4, May
I I -May 17
• Phase 2 Application - May 5 - May 11,
2000
• Post Test Sampling - June 2 and June 21-22,
2000, Sept 2000, October 2000, March
2001
thl4group.
17
BUILDING
wo
v� • / `MItST1,00
LOCATION
2\ BUILDING r•` ��1�`�'
Z,� BUILDING 6 }1
Ot^ • sw _22 O �P°°yrt_,��M_a 5v� _z 0 Of -
BUILDING
NIY�
�0 NO
RO`UNOS
\ FORMER GASOLINE
\\ RCp UST LOCATION
q5
\
\ P
\ 9
\
li \\ 05
F�
I \\ 2
\ 2
I \ �
Z9
\
\
I \
\
\\ QC
O
N
I \
\
EO P N MENt
PHASE 1
4
BUILDING
9
2C,
1 5
40
PAVE
GRAPHIC SCALE
20 910 20 M
( IN FEET )
�y
�P
ti
J2
Q
ASPHALT PAVEMENT
II
IT CORPORA— OF
CA —NA .
i2oa GlilE Y GEXIRE BLw.
sum 203
RSALLE. 2NJN1 N[
(9191 1DT-2227
LEGEND
MONITORING NETWORK
WELL LOCATION MAP
MONITORING POINT
G INJECTION POINT
W.P. BALLARD PROPERTY
° OREENSBORO, NC
a[KD L n: DRNILD fix: <xECNm DY:
DIRNW
�A qMS/00
K�TSSSWEu52
ND�c
10]5}S
Nam:
FIG. 3
the vf*oup 18
BUILDING"
o 0-
V�'w
BUILDING
FORMER
PO B
7
-11: PCE AST LOCATION
BUILDING
ABUILDING
10111\lr" BOND
FORMER GASOLINE
RCP UST LOCATION
70
9\
0-
BUILDING
f.
92
Ss PAVE
GRAPHIC SCALE
IN FELT
by
BUILDING ze
/ ASPHALT PAVEMENT
III
PHASE 2
—
10RSV
NaRNSnLLL W 275W
LEGEND
PHASE 2
• MONITORING POINT
NJECTION POINTS
0 INJECTION POINT
W.P. SALIM PROPERTY
GREENSBORO, NC
M
DMONsr
DIE IDUARLDNW- C O_
9/5/00 mw.—
FIG. 4
the v1*0up 19
Results of Pilot Test
• permanganate safely injected from 65 feet
to within 15 ft of surface with a Geoprobeg
• no significant increases in subsurface
temperature or pressure
• some gaseous byproducts produced in
subsurface, particularly where petroleum
present, but dissipated quickly
0
`"evig'r-oup
20
Results of Pilot Test (Cont'd)
• permanganate oxidized VOCs in
groundwater and soil
• reduced Total VOCs in 20 of 24
groundwater wells
— 12 wells reduced by > 60%
— 3 wells reduced by >90
• Total VOCs increased in several wells
the�i oup 21
FIGURE 7
COMPARISON OF PRE -AND POST -INJECTION TOTAL VOCS IN GROUNDWATER
INJECTION ZONE SHALLOW MONITORING WELLS
WP BALLARD AND DOWNGRADIENT PROPERTIES, GREENSBORO, NORTH CAROLINA
250,000
200,000
cm
3
z 150,000
O
cc
z
w
U
z
0 100,000
U
O
50,000
�0
the MW-1 MW-2
i t-11 p
-40%
602%
907%
-244°o
MW-3 MW-4 MW-5
76'
■ PRE-INJ Total VOCs 03/22/00
■ POST-INJ Total VOCs 06/23/00
❑ POST-INJ Total VOCs 09/06/00
o POST-INJ Total VOCs 03/06/01
77°0
34%
8°
222%
MW-6 MW-10 PT-3S PT-4S PT-5S SVE-8 SVE-9
WELL NUM BER ��
88%
51 °%
120,000
100,000
80,000
60,000
z
O
U
UO 40,000
20,000
FIGURE 8
COMPARISON OF PRE -AND POST INJECTION TOTAL VOCS IN GROUNDWATER
INJECTION ZONE DEEP MONITORING WELLS
W. P. BALLARD AND DOWNGRADIENT PROPERTIES, GREENSBORO, NORTH CAROLINA
■ PRE-INJ Total VOCs 03/22/00
18% ❑ POST-INJ Total VOCs 06/23/00
❑ POST-INJ Total VOCs 09/06/00
❑ POST-INJ Total VOCs 03/06/01
34% 58%
69%
8%
99%
62% -66°•0
1 / 47%
55% - _7i%
1 1 12%
-4% 92°
39% -43%
-32%
1/14
)% 52% 0%
-14%
-° 56%
-22% %
DW-1 DW-2 DW-3 DW-4 BMW-1 BMW-2 PT-1 D PT-21D PT-31D PT-41D PT-51D HVDP- HVDP-
13 14
the Ou WELL NUMBER
�O�' p 23
VOC Increases in Source Area
• higher oxidation demand due to presence of
petroleum hydrocarbons
• insufficient permanganate injected to
oxidize both petroleum & solvent
• oxidation of organic carbon reduces
partitioning coefficient
0
`''QOg-oup
24
Implementation Schedule
• In situ Oxidation Application
— Pilot - 2000
— Full Scale
• Phase 1
- Jan -
July
2001; Phase 2 - Aug - Dec 2000;
Phase 3
- Jan -
June
2002
• HVDP/SVE
• Permitting/Installation - 2000
• O&M/Monitoring /Reporting -Start Jan 2001
•� Goal -Achieve Remedial Goals -September 2002
the Ogro up. 25
--------- --
ASPH PAVEMENT
AND CRETE
186)
-------------
8
\
has'
I --=
/
BUILDING
NOTES:
HORIZONTAL DATUM IS NAD .83.
VERTICAL DATUM IS NOVO 28.
THIS IS NOT A BOUNDARY SURVEY.
NOT FOR RECORDATION.
MAPPING SCALE : 1 INCH - 60 FEET.
MAPPING CONTOUR INTERVAL SHOWN HEREON = 2 FEET.
PROPERTY LINE FROM PLAN ENTITLED "ALTA/AGSM LAND FO TITLE SURVEY R: GREENSBORO D.C. PARTNERS, LTD.-,
DATED 5/12/95 PREPARED BY ROBERT E. WILSON. INC.
r --
Full-Sc1'e Phasing_ • � lan _ PROPER`r LINE (TYPICAL)
Phase I - Jan - July
LEGEND
Q 2001 1286) TOTAL VOC CONCENTRATION
/—
—IC'O—— —TOTAL VOC CONCENTRATION CONTOUR /
Phase 11- July - NOT DETECTED
\
Dec 2001 ®
o�
NOTE:
/ DMP-I. DMP-2, DMP-3 AND DMP-4 E
Phase III - Jan - SAMPLED ON 1/21 /99 D
June 2002 GRAPHIC SCALE ° ---T
\/ BO 0 30 BO 120
\ ( IN FEETO) O Exlcnxc iaox Hvc III
\ � sxxW� xuE
thevf*oup 26
Phase I Full Scale Injection Plan
• 45 Geoprobe Points
• 5% Sodium Permanganate Solution
• 32 Gallons per 5 foot Interval
0
`"eOgroup
27
Phase II Full Scale Injection Plan
• 50 Geoprobe Points
• 10% Sodium Permanganate Solution
• 50 Gallons per 5 foot Interval
0
`"eOgroup
W.
Phase III Full Scale Injection Plan
• 30 Geoprobe Points
• 15% Sodium Permanganate Solution
• 52 Gallons per 5 foot Interval
0
`''QOgroup
29
Proposed Phase III Injection Plan
Injection Design Calculations
Calculation Parameters
• Contamination -Related Parameters
• Site -Related Parameters
• Oxidant -Related Parameters
• Application -Related Parameters
0
the �igroup.
30
Proposed Phase III Injection Plan
Injection Design Calculations
Contamination -Related Parameters
• Nature of Contamination
• Mass of Contamination
0
the(49roup.
31
Proposed Phase III Injection Plan
Injection Design Calculations
Contamination-Related Parameters
Nature of Contamination
• Chlorinated Solvents
PCE (Primary)
— TCE & 1,2-DCE (Secondary)
• Petroleum Hydrocarbons
0
`''eOgroup
32
Proposed Phase III Injection Plan
Injection Design Calculations
Contamination -Related Parameters
Mass of Contamination
• Degree of Impact
• Type of and Characteristics Impacted Media
• Volume of Impacted Media
0
`''Q(4group
33
Proposed Phase III Injection Plan
Injection Design Calculations
Degree of Impact
• Concentration in the Vadose Zone
— Sorbed Phase Concentration
— Vapor Phase Concentration
• Concentration in the Saturated Zone
— Dissolved Phase Concentration
Sorbed Phase Concentration
`''Qig'r-oup
34
Proposed Phase III Injection Plan
Injection Design Calculations
Type and Characteristics of Impacted Media
• Saturated versus Unsaturated
• Degree of Saturation
• Bulk Density of Soil
• Porosity of Subsurface Media
• Organic Carbon Content (Partitioning)
0
the
(Pgroup-
35
so we
Proposed Phase III Injection Plan
Injection Design Calculations
Volume of Impacted Media
• Vadose Zone Thickness
• Saturated Zone Thickness
• Surface Area
• Bulk Density of Soil
• Porosity of Subsurface Media
the
(4 ou � gar p6
1
Injection Design Calculations
Calculation Parameters
Site -Related Parameters
• Surface Area of Phase III Site
• Vadose Zone Thickness
• Saturated Zone Thickness
• Site Geology and Hydrogeology
• Water -Filled Porosity
• Organic Carbon Content (Partitioning)
• Subsurface pH
`''Q�igroup
J%
i
Injection Design Calculations
Calculation Parameters
Oxidant -Related Parameters
• Oxidant Chemical & Physical Properties
— Specific Gravity
— Molecular Weight
— Water Solubility
— Concentration of Row Material
• Stoichiometric Reactions with Site Contaminants
• Natural Soil Demand
0
the0group. 38
Injection Design Calculations
Calculation Parameters
Oxidant -Related Parameters
Stoichiometric Reactions with Site Contaminants is pH -
Dependent: In the pH Range from 3.5 to 12
PCE: 4NaMn04 + 3C2C14 + 4H2O ---> 6CO2 + 4Mn02 + 4Na+ + 12C1- + 8H+
TCE: 2NaMn04 + C2HC13 --- > 2CO2 + 2Mn02 + 2Na+ + 30- + H+
DCE: 8NaMn04 + 3C2H2C12 --- > 6CO2 + 8Mn02 + 8Na+ + 60- + 20H- + 2H2O
VC: 10NaMn04 + 3C2H3C1 ---> 6CO2 + 10Mn02 + 10Na+ + 3C1- + 70H- + H2O
Note: PCE, As the Primary Site Contaminant, its Reaction with Permanganate Controls the the Overall
Oxidation Process. Mass Stoichiometric Ratio is: 1.1 pounds NaMn04 Per Pound PCE.
t& 0AWOUP.
39
Injection Design Calculations
Calculation Parameters
Application -Related Parameters
• Injection Method
• Injection Flow Rate
• Injection Volume
• Number of Injection Points
• Number of Injection Intervals
0
th,e(4oup 40
Injection Design Calculations
Calculation Parameters
Application-Related Parameters
Injection Method
• Direct Push Using Geoprobe
• Infiltration Gallery
• `41
''Q�igr-oup
Injection Design Calculations
Calculation Parameters
Application -Related Parameters
Injection Flow Rate
• Geoprobe Pilot Injection Test
• Site Hydrogeologic Properties
• Pilot Injection Test
Optimum Injection Flow Rate is 2 GPM
0
`''eOgroup
42
M
Injection Design Calculations
Calculation Parameters
Application -Related Parameters
Injection Volume
• Mass of Contamination
• Concentration of Oxidant Working Solution
• Natural Soil Demand
0
the(49roup.
43
Injection Design Calculations
Calculation Parameters
Application -Related Parameters
Number of Injection Points
• Area to be Treated
• Site Accessibility
• Radius of Influence
• Treatment Level
• Injection Pressure
0
`''Q�ig'r-oup
Injection Design Calculations
Calculation Parameters
• Bench Scale Testing
— Contaminant Demand
— Natural Soil Demand
Treatment Level
• J
Geoprobe Injection Testing
— Radius of Influence
Attainable Depth
• Pilot Injection Test
Treatment Level
— Application Method
— Full Scale Application Design
the oup 45
Phase III Injection Plan
Contingency Plan
• Re -Injection Using the Geoprobe Method
• Re -Injection Using Infiltration Gallery
• Re -Injection Using Existing Site Wells
0
`''eOgr-oup
Regulatory Approval Status - General
• Well permits - obtained in 1998 and 1999
• Comprehensive Site Assessment -
submitted December 1999; acceptance
received April 2001
• Corrective Action Plan - submitted May
1999; approval pending
the (491roup- 47
Regulatory Approvals Status - HVDP
System
• ROW Encroachment Agreement - obtained
April 2000
• Air Discharge permit - obtained May 2000
• NDPES Authorization to Construct -
obtained September 2000
• Building permits - obtained June 2000
0
the0" oup 48
Regulatory Approval Status - In Situ
Oxidation with Permanganate
• UIC permit -
— obtained for pilot in March 2000;
— received for Phase 1 and 2 in April 2001
— pending for Phase 3
0
the (49roup.
49