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87th Air Base Wing Joint Base McGuire-Dix-Lakehurst Restoration Advisory Board 8 December 2016
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87th Air Base Wing

Joint Base McGuire-Dix-Lakehurst Restoration Advisory Board

8 December 2016

87th Air Base Wing

Mr. Curtis Frye, P.E.Chief, JBMDL Environmental Restoration Program

AFCEC/CZOE

Review of Action Items

3“WIN AS ONE”

Action Items BOMARC Sites OT016, WP005, and ST015

Surface Water Evaluation Inquiries were made during the August 2016 RAB

meeting with respect to the sampling history and delineation efforts within the BOMARC study area. Arcadis has prepared a presentation to brief the RAB on the BOMARC surface water evaluation to address these questions

4“WIN AS ONE”

Action ItemsMr. Tamn had requested an update on any

fuel line leaks at McGuire The Remedial Investigation Report for OU-6

addresses the impacts from historic fuel line leaks. This document is currently being finalized. The draft Remedial Investigation was published in 2014 An OU-6 overview will be presented tonight in

the JB MDL PBR Contract Basewide Update

87th Air Base Wing

Mr. Tim Llewellyn, Project ManagerARCADIS

Update on McGuire Operable Units 1 and 3 Landfill Sites

6

Agenda(OU1 and OU3 Landfill Sites)

Overall Project Status

Site location and nomenclature

Site history and current conditions

Discussion of pertinent site data (OU1 only)

Discussion of the Remedial Alternative Development

7

In 2014, the Operable Unit 1 (OU-1) and Operable Unit 3 (OU-3) Feasibility Studies (FS) for OU1 and OU3 were at Draft and Draft Final iterations

Arcadis resumed work on (F)FS documents:

• Revised to reevaluate data to the Class I-PL standards

• Additional samples collected during July/November 2016

• OU-1 – Internal Draft in review with Air Force

• OU-3 – Draft Final in review with regulatory agencies

Overall Project Status

8

Location and NomenclatureOperable Unit 1 (OU-1)

Operable Unit 1 (OU-1), Landfill Sites LF-03 – Landfill No. 2 LF-04 – Landfill No. 3 ST-07 – Former Defense Reutilization

Marketing Office (DRMO)

9

OU-1 Site History(LF-03,ST-07, and LF-04)

LF-03/ST-07• Operated from 1950 - 1960s• Trench and fill• Mixed municipal waste• Generally a continuous waste mass• ST007: PCB removal action conducted during 2011

LF-04• Operated for a shorter duration 1956/57• 8 discrete waste burial pits

10

OU-1 Recent Investigations

LF-03• Baseline Ecological Risk Assessment • Surface water sampling and culvert investigation• Installation of a new monitoring well• “Pinelands” groundwater sampling• Slope stability analysis and landfill cover assessment

LF-04• Baseline Ecological Risk Assessment• Surface water sampling• “Pinelands” groundwater sampling

11

OU-1 Current Site Conditions

LF-03• Generally flat with the exception of the North Run

Embankment • Mixed open fields with heavy vegetation• North Run embankment• Groundwater flows to the North Run

LF-04• Gently sloping topography and heavily forested• Bisected by Defense Access Highway• Groundwater flows to the North Run

12

OU1 – Site Layout(LF-03/ST-07)

LF-03

ST-07

Groundwater Flow

13

Current Landfill Cover ConditionsLF-03/ST-07

Photo taken 01/2015; facing west

14

Current Landfill Cover ConditionsNorth Run Embankment

Photo taken 01/2015; facing north toward North Run

15

North RunAdjacent to LF-03

Photos taken on 11/23/2016

16

North RunCulvert (LF-03)

Photo taken on 04/2015

17

OU-1 – Site Layout(LF-04)

18

Landfill Cover ConditionLF-04

Photo taken on 04/2015

19

North RunLF-04

Photos taken on 04/2015

20

Surface Water Sample Results

Screening Criteria• Pineland non-degradation standards (e.g., Practical

Quantitiation Limit (PQL) and Background Threshold Values (BTVs)

• Health Based Standards (e.g., NJDEP Fresh Water Acute Toxicity and EPA MCL [Drinking Water Standard])

Metals• Excludes nutrient metals (e.g., potassium, calcium,

magnesium, sodium) • Higher of the BTV or PQL

BTV: Background Threshold ValuePQL: Practical Quantitation Limit

MCL: Maximum Contaminant Limit

21

OU-1 – Surface Water Sample Results(LF-03)

SW-37- Toluene = 1.8

- >PQL (1.0)- <MCL (1,000)

- Pyrene = 0.54; >PQL (0.1)- Arsenic = 3.3; >PQL (3.0), <MCL (10)- Iron = 45,000; >BTV(4,990)

SW-38SW-39

SW-01

SW-02

SW-03

Culvert

All units are in parts per billion

22

OU-1 – Surface Water Sample Results(LF-03)

SW-37

SW-38SW-39

SW-01

SW-02

SW-03

Culvert

Chlorobenzene = 2.1- >PQL (1.0)- <MCL (100)

All units are in parts per billion

23

OU-1 – Surface Water Sample Results(LF-04)

SW-05SW-06

Bis(2-Ethylhexyl)phthalate = 8.7- >PQL (3.0)- >MCL(6.0)

All units are in parts per billion

24

OU-1 Focused Feasibility Study (FFS) Summary and Alternative Development

25

OU-1Use of a Presumptive Remedy

Question: What is a presumptive remedy?Answer: Preferred technologies for common categories of sites (e.g., landfills)

Presumptive remedies streamline the remedy selection process (i.e., removal not considered as an option)

Evaluates technologies that are best suited for the site Ensures consistent selection of remedial actions Landfill sites must exhibit “appropriate”

characteristics for applicability of a presumptive remedy (e.g., type of waste, volume, low risks/hazards)

26

Alternative1 Summary

Alternative 1: No Action

• Required• Establishes a baseline to compare the other alternatives

Alternative 2: Optimized Soil Cover

• Ensure a minimum 1 ft to 2 ft of existing soil cover over the buried waste

• Conduct a landfill cover verification investigation• LF-03: Stabilize slope along North Run embankment

Alternative 3:2 Foot (ft) Soil Cover

• Install a 2-ft soil cover over the waste, regardless of existing soil cover

• Prevents direct contact of buried waste, does not prevent infiltration of stormwater through waste

• Clear cut forests at both sites to prepare for cap installation• LF-03: Stabilize slope along North Run embankment

Alternative 4:RCRA Subtitle D Landfill Cover

• Install a 2-ft thick RCRA Subtitle D Cover• Typical “landfill” cover• Prevents infiltration of stormwater• LF-03: Stabilize slope along North Run embankment

1Only the substantively different aspects of the proposed alternatives are discussed

Proposed Remedial AlternativesOU-1

27

Alternative 2 - Optimized Soil CoverLF-03/ST-07

28

Subgrade Plan for Alternatives 3 and 4 LF-03/ST-07

29

Final Grading Plan for Alternatives 3 and 4LF-03/ST-07

30

Alternative 2 - Optimized Soil CoverLF-04

Key Assumption: only a portion of the buried waste will need additional fill

31

Subgrade Plan for Alternatives 3 and 4LF-04

32

Final Grading Plan for Alternatives 3 and 4LF-04

33

OU-1 Path Forward

Date Activity

Nov 18, 2016 Internal Draft FFS submitted to JB MDL

Jan 2017 Draft FFS submitted for regulatory review

April 2017 Finalize FFS

Aug 2017 Finalize Proposed Plan

Feb 2018 Finalize Record of Decision

34

Operable Unit 3 (OU-3) Discussion

35

Location and NomenclatureOperable Unit 3 (OU-3)

Operable Unit 3, Landfill Sites LF-02 – Landfill No. 4 LF-19 – Landfill No. 5 LF-20 – Landfill No. 6 WP-21 – Former Waste Water

Treatment Plant Disposal Area

36

Operable Unit 3 (OU-3) Site History

Operational Dates

• LF-02 (Landfill No. 4): 1958 and the early 1970s

• LF-19 (Landfill No. 5): 1970 to 1973

• LF-20 (Landfill No. 6): 1973 to 1976

• WP-21(Former Waste Water Treatment Plant Disposal Area): 1970’s to 1980’s; decommissioned in 1994

37

Operable Unit 3(OU-3) Recent Investigations

Additional 11 monitoring wells installed during 2012

“Pinelands” groundwater sampling – two rounds during 2016

Annual landfill inspections conducted for 2015 and 2016

38

Operable Unit (OU-3) – Site Layout

LF-19

LF-20

LF-02WP-21

39

Current Landfill Cover Conditions

LF-02: Photo taken 11/2016; facing southeast

LF-19: Photo taken 11/2016; facing southeast

40

Alternative1,2 Summary

Alternative 1: No Action

• Required• Establishes a baseline to compare the other alternatives

Alternatives 2, 3, 4:2-ft Soil Cover

• Similar to the soil cover proposed at OU-1• Install a 2-ft soil cover over the waste, regardless of existing

soil cover• Soil removal for Alternative 3

Alternative 5, 6, 7:RCRA Subtitle D Landfill Cover

• Similar to the cap proposed at OU-1• Install a 2-ft thick RCRA Subtitle D Cover• Typical “landfill” cover• Prevents infiltration of stormwater• Soil removal for Alternative 6

1Only the substantively different aspects of the proposed alternatives are discussed2Individual alternatives are proposed for the three landfill sites but use consistent technologies

Proposed Remedial AlternativesOU-3

41

OU-3Soil Removal for Alternatives 3 & 6

LF-02

WP-21

WP-21

42

OU-3 Surface Water Sample Locations

LF-19

LF-20

LF-02WP-21

SW-A

SW-B

SW-C

43

OU-3 Path Forward

Date Activity

Oct 31, 2016 Revised Draft Final FS submitted for regulatory review

Dec 2017 Finalize FS

May 2017 Finalize Proposed Plan

Sept 2017 Finalize Record of Decision

44

Questions?

87th Air Base Wing

Mr. Tim Llewellyn, Project ManagerARCADIS

Review of BOMARC Surface Water Data

46“WIN AS ONE”

BOMARC Surface Water

OT016, WP005, and ST015 Surface Water Evaluation

This presentation has been prepared to address these questions posed during the August 2016 RAB meeting with respect to the sampling history and delineation efforts within the BOMARC study area

47“WIN AS ONE”

BOMARC Surface Water Questions

What are the concentrations of TCE in surface water

When was the last time surface water data was collected and are the trends declining

How far downstream has sampling been completed and are the downstream areas impacted

48“WIN AS ONE”

BOMARC Site Location

BOMARC SITE

49“WIN AS ONE”

BOMARC Site Plan

Residual TCE areas

Dissolved Phase TCE groundwater plume

50“WIN AS ONE”

BOMARC Conceptual Site Model

51“WIN AS ONE”

Regional WatershedBOMARC SITE

Surface waters from BOMARC discharge to Success Branch generally moving north/northeast to Borders Mill Branch to Ridgeway Branch ultimately feeding into Union Branch and Toms River

General Flow Direction TCE Plume Discharge Area

52“WIN AS ONE”

Summary of Detections

The highest TCE detection observed to date was in 2009 at SW-11 (186 parts per billion [ppb])

Limited detections of TCE degradation products (1,2-dichloroethene and vinyl chloride) observed in groundwater and surface water

Other than the 186 ppb detection in 2009, TCE detections in the primary/secondary plume discharge areas fluctuate between non-detect and 72 ppb (SW-13 – 2002)

Upstream sampling of Elisha Branch at 10 locations and the unnamed tributary at 5 locations between 1999 –2014 have confirmed these portions of the stream are not significantly impacted

53“WIN AS ONE”

Summary of Detections Continued

Sampling of Success Branch immediately downstream of the plume discharge areas conducted between 2001 and 2014 has confirmed TCE impacts

TCE concentrations continue to decline further downstream in Success Branch and Borders Mill Branch to the north/northeast and areas further away from the primary/secondary plume discharge areas but TCE is present

Overall, TCE detections observed between 1999 and 2014 show declining trends

54“WIN AS ONE”Maximum TCE detection (186 ug/L) at SW-11 in 2009

TCE Detections in ppb (1999 – 2014)

Primary Plume Discharge Area

Secondary Plume Discharge Area

55“WIN AS ONE”Maximum TCE detection (186 ug/L) at SW-11 in 2009

TCE Detections in Primary/Secondary Plume Discharge Areas

Secondary Plume Discharge Area

Primary Plume Discharge Area

56“WIN AS ONE”

TCE Detections Upstream Areas

TCE detections at upstream locations along Elisha Branch were all below 1 ppb.

57

TCE Detections Downstream Areas

Further downstream (~1,500 feet) of TCE plume discharge areas (TCE ranged from non-detect to 12 ppb)

Immediately downstream of TCE plume discharge areas (TCE ranged from non-detect to 34 ppb)

58“WIN AS ONE”

TCE Trend at SW104 (primary plume discharge area)

0

10

20

30

40

50

60

7/6/2009 1/22/2010 8/10/2010 2/26/2011 9/14/2011 4/1/2012 10/18/2012 5/6/2013 11/22/2013 6/10/2014 12/27/2014

TCE

(ug/

L)

Date

OT16-SW104

59“WIN AS ONE”

TCE Trend at SW105 (primary plume discharge area)

0

10

20

30

40

50

60

70

4/19/2001 1/14/2004 10/10/2006 7/6/2009 4/1/2012 12/27/2014 9/22/2017

TCE

(ug/

L)

Date

OT16-SW105

60“WIN AS ONE”

Surface Water TCE Screening Criteria

Using the latest TCE toxicology values from USEPA Guidance published in 2014 the calculated risk-based level for a recreational exposure scenario to surface water is 38.3 ppb

Of the 61 locations samples between 1999 and 2009, 4 locations have exhibited TCE concentrations in exceedance of the recreational risk-based level

All 4 locations with TCE detections above the risk-based level are located within or directly downstream of the plume discharge area and limited to Success Branch

TCE has not been detected above the calculated risk-based level (38.3 ppb) since October 2009

61

Questions?

87th Air Base Wing

Mr. Tim Llewellyn, Project ManagerARCADIS

JB MDL PBR CONTRACT UPDATE

63“WIN AS ONE”

McGuire Summary

NPL Site StatusOU# Description Final FS Final PP Final ROD

OU1 3 Landfill Sites Under AF review Summer 2017 Winter 2018

OU2 10 Industrial Sites Summer 2017 Winter 2018 Summer 2018

OU3 4 Landfill Sites Under EPA/NJDEP review Spring 2017 Fall 2017

OU4 1 Jet Fuel Storage site Summer 2017 Winter 2017 Summer 2018

OU5 3 Misc. Sites Fall 2017 Winter 2018 Summer 2018

OU6 Fuel Spills under Apron Fall 2017 Winter 2018 Fall 2018

OU7 4 Industrial Sites Fall 2017 Winter 2018 Fall 2018

OU8 5 Sites on the Airfield Fall 2017 Winter 2018 Fall 2018

64“WIN AS ONE”

McGuire SummarySecond major groundwater sampling event completed in November

Total of 10 weeks in the field with 3 crews sampling a total of approximately 600 wells The new data was required to fully evaluate

compliance with the Pineland Standards Data will be used for remedy evaluation in the FS

documents Data evaluation now in progress and NPL

documents moving forward

65“WIN AS ONE”

McGuire Summary NPL Sites (Continued)

Pilot scale tests of potential remedies are complete at several sites Multiphase extraction at OU2 (solvents) Natural Source Zone Depletion at OU4

(jet fuel) Phase I: In-Situ Microcosms/enhanced

bioremediation at OU7 and OU8 (dissolved phase solvents)

66

OU6 Historical Fuel Spills

Operable Unit 6, Site ST022 (Aircraft Apron Fuel Line Break) Several rounds of groundwater sampling

completed (~60 wells) to assess current nature and extent of hydrocarbons in groundwater under the PBR in 2015/2016

67“WIN AS ONE”

Summary of Historical OU6 Releases

SS030 (Fuel Hydrant System South of Bldgs 2251 and 2253)

• No known fuel release. The site was identified based on elevated soil gas readings during siting of a new hydrant system

SS031 (Fuel Hydrant System South of Buildings 1712 and 1732)

• JP-4 refueling spill in 1981. Exact location of release unknown• Other possible sources related to hydrant system leakage, though no

other releases reported

68“WIN AS ONE”

Summary of Historical OU6 Releases

16 December 201668

SS032 (Underground Surface Water Pipes, Former Stream Beds, Hydrant Crossings)

• No reported release, however the drainage feature controls shallow groundwater direction and potentially provides a preferential pathway for contaminant transport

SS033 (Buildings 1750 and 1751)• Small surface spills of hydrocarbons reported related to maintenance

activities. One surface release (~10 gal) entered floor drain and into an oils/water separator

ST022 (Aircraft Apron Fuel Leak)• JP-4 Fuel line rupture with an unknown (but significant) quantity of

JP-4 released

69“WIN AS ONE”

Location of Groundwater Plumes

ST-22JP-4 Release

1988

SS-30 Elevated Soil

Gas 1995

SS-31No release reported but coincident

with hydrant system pipeline

SS-31Possible location of

refueling spill

SS-33Supply warehouse and

maintenance/repair; small spills

70“WIN AS ONE”

OU-6 Path Forward

CERCLA Document Status

• Remedial Investigation Report – Draft Final version to be submitted to EPA early 2017; Final by February/March 2017

• Feasibility Study – Final by September 2017

• Proposed Plan – Final by February 2018

• Record of Decision – Final by September 2018

71

McGuire State Led Petroleum Storage Sites

Implemented Remedies Monitored Natural Attenuation

Four sites (coming up on 1st year) (CF-11; SS-15; TU-20; TU-25)

AS/SVE One site (TU-13-UST E112)—operating and

removing petroleum contamination ISCO

One site (TU-18-Bld. 3438 Gas Sta.)—one of three injections complete

Biosparging One site (TU-23-Pumphouse B) under

construction and will be operational in February 2017

Remedies under Design Excavation/MNA

One site (TU-03 UST at Bld. 2913)—Soils excavation planned for Winter 2017

Site Closeout One site closed (DP501-Bld. 1907) Close out memo under review (TU-22-UST

E187)

TU-13 (UST E112) – Cumulative Mass Removed (lbs)

0

40

80

120

160

200

6/19/2016 7/19/2016 8/19/2016 9/19/2016 10/19/2016

Mas

s Rec

over

ed (l

bs)

72“WIN AS ONE”

BOMARC Update Feasibility Study under NJDEP review OT-16 (Missile Launcher),

WP-05 (JP-X Discharge Pit), and ST-15 (MOGAS UST)

BOMARC SITE

73“WIN AS ONE”

BOMARC SITE LAYOUT

OT016

WP005

74“WIN AS ONE”

POTENTIAL REMEDY FOR OT-16 (Missile Launcher) and WP-05

(JP-X Discharge Pit)

Proposed Air Sparge Lines—Conceptual Design

Containment Area

75“WIN AS ONE”

BOMARC OT-16/WP-05 SCHEDULE

Feasibility Study Draft FS to NJDEP September 2016 (delayed from May to enable discussions

ahead of submittal) Final FS Winter 2016/2017

Proposed Plan Draft to NJDEP February 2017 Final PP (and public meeting) June 2017

Record of Decision Draft to NJDEP September 2017 Final ROD January 2018

Remedial Action Winter 2018

76“WIN AS ONE”

Dix Update Air Sparge Systems (TU-19a—Former Taxi Stand)

AS/SVE systems operational at all three sites.

0.00

50.00

100.00

150.00

200.00

250.00

Mas

s Rec

over

ed (l

bs)

TU-19a - Cumulative Mass Recovered (lbs)

Cumulative Mass Recovered (lbs)

77“WIN AS ONE”

Dix Update Air Sparge Systems (TU970—Bld. 6045)

AS/SVE systems operational at all three sites. 0.00

10.00

20.00

30.00

40.00

50.00

60.00

Mas

s Rec

over

ed (l

bs)

TU970 - Cumulative Mass Recovered (lbs)

Cumulative Mass Recovered (lbs)

78“WIN AS ONE”

Dix Update Air Sparge Systems (NW-44—Bld. 5136)

AS/SVE systems operational at all three sites. 0.00

20.00

40.00

60.00

80.00

100.00

120.00

140.00

160.00

Mas

s Rec

over

ed (l

bs)

NW-44 - Cumulative Mass Recovered (lbs)

Cumulative Mass Recovered (lbs)

79“WIN AS ONE”

Lakehurst Update

Areas A/B and C Semi-Annual sampling completed in

October 2016 Active remedies being designed for

4 sites to meet GW standards by 2021. Draft designs nearly completed for 3 of the 4 sites.

Pre-Design investigations complete at all 4 sites

Pilot Studies complete at 3 of 4 sites MNA remedies approved from 2

sites to meet GW standards by 2021Area D Annual GW sampling completed in

November 2016

80“WIN AS ONE”

Lakehurst Update

Area H Active pump and treat system

continues to operate Semi-Annual sampling

completed in October 2016

Areas I/J and K Annual GW sampling

completed in November 2016

81“WIN AS ONE”

Lakehurst Update

Soil collected during Area C Site AT016 Pre-Design Investigation Work

Groundwater Sampling to Support Design Investigations at Area C

82

Basewide Activities

Base-wide Well Inspection Ongoing (Well FT at Area D)

Biennial well survey in progress• ~2000 monitoring

wells at JB MDL• All will be inspected

and repaired as needed

83

Questions?

84

RAB Agenda Ideas

“WIN AS ONE”

Tentative RAB date: 2017 schedule is to be determined Suggested agenda topics

85

PUBLIC COMMENTS


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