KIRTLAND AIR FORCE BASE ALBUQUERQUE, NEW MEXICO ...

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SECTION 2 • KAFB-1068 3.8-ft SVE • KAFB-1066 2.45-ft • KAFB-1065 3.33-ft SVE • KAFB-10614 0.23-ft. • KAFB-1069 0.79-ft. • KAFB-10610 1.18-ft. • KAFB-10618 (sheen) Measured thicknesses are greater at monitoring wells where active SVE is ongoing, producing a mounding effect. The LNAPL plume extends approximately 2,600 ft long and is approximately 1,000 ft wide, trending along the groundwater flow direction. 2.4.6 Dissolved Phase COPC Distribution The distribution of dissolved-phase contaminants forms a halo around the LNAPL plume. As expected, concentrations of dissolved COPCs are detected at high concentrations very close to the LNAPL plume due to the dissolution of petroleum products into the groundwater and lower concentrations further from the LNAPL plume. The dissolved-phase plume extends approximately 4,500 ft along the axis of the plume, trending along the groundwater flow direction. EDB is the most widely distributed COPC. The footprint of the dissolved-phase plume downgradient is elongated as the more mobile contaminants such as benzene and EDB are more quickly transported along with groundwater movement downgradient. The dissolved phase plume is shown on Figure 2-7. 2.4.7 Site Specific Fate and Transport In aerobic and anaerobic environments, benzene, toluene, ethylbenzene, xylenes (BTEX) can be degraded by microorganisms. Kinetic rates of BTEX degradation are highest under aerobic conditions. The natural abundance of electron acceptors like nitrate, manganese, iron, and sulfate are typically higher than contributions from oxygen and are typically more than sufficient to stabilize the advancement of a dissolved petroleum hydrocarbon plume (Rice et al., 1995; Mace et al., 1997; NRC, 2000). Methanogenesis is unique in that carbon dioxide, a biodegradation byproduct, is both produced and used as an electron acceptor. Thus, if methanogenesis is occurring at a site, electron acceptor limitations will not be expected to occur until all petroleum hydrocarbons and carbon residuals are fully degraded. EDB can degrade via aerobic and anaerobic biodegradation and abiotic hydrolysis. In the vadose zone at BFF, aerobic biodegradation is expected to be a significant transformation mechanism. Natural fluctuations in barometric pressures create pressure differentials between the atmosphere and the subsurface, promoting air exchange and oxygen transfer. Biological sampling in the vadose zone has determined that a robust bacterial community that can contribute to degradation of hydrocarbons is present. In the saturated zone, both aerobic and anaerobic biodegradation are expected to occur (CH2M HILL, 2009). The fuel “type” indicates that the release started before 1981 because of the presence of AvGas on the water table. EDB is detected on the leading edge of the plume, indicating that the source is AvGas. The presence of EDB and the lack of BTEX compounds are indicative of the natural attenuation occurring on the edges of the dissolved plume. EDB is a recalcitrant compound and slow to naturally attenuate by microbial means. Vertical migration of LNAPL from the source area/release through the vadose zone is the primary mechanism of contaminant transport within the vadose zone at Kirtland AFB. The release of fuels in the source area was stopped in 1999. Residual fuel in the vadose zone will be entrapped by capillary forces in Kirtland AFB June 2010 Groundwater Investigation Work Plan BFF 2-8
SECTION 2 the soils. Only that part of the fuel that is present in the vadose zone at greater than residual saturation will continue to migrate. A secondary transport mechanism within the vadose zone in the source area is within the soil vapor. Vapor phase contamination occurs as contaminants partition from entrapped LNAPL and soil water into soil gas. Vapor phase contamination will disperse in an approximately spherical pattern through the vadose zone surrounding the source area. For this reason, additional monitoring points have been located radially around the source area and vertically across the vadose zone to allow delineation of this spherical vapor plume. In addition to vapor migration vertically down to the groundwater table, vapor migration vertically upwards to the ground surface also is a potential. Groundwater flow and hence contaminant transport is affected by both the regional groundwater flow and the localized effects of induced groundwater flow from pumping. Locally, the effects of pumping can induce increased gradients vertically and laterally. Transport of dissolved contaminants will be affected by both physiochemical retardation and biodegradation. 2.5 Potential Receptors The Veterans Administration (VA) Medical Center water well and KAFB groundwater production wells KAFB-15 and KAFB-16 are located sidegradient of known areas of petroleum hydrocarbon contamination. The VA Medical Center Water well, KAFB groundwater production wells, and water utility authority well fields will be considered potential pathways of exposure until they can be excluded with defensible data. During the second quarter 2009 sampling, TPH-DRO was the only chemical detected in KAFB-16 well at 0.26 micrograms per liter (µg/L) but it was determined that this contaminant was likely introduced into the well through lubricating oil used for lubrication of the well pump. Water production wells KAFB-3 and Burton Well W-5 are located 3,800 and 3,700 ft, respectively, downgradient of the leading edge of the EDB plume and 5,400 ft and 4,800 ft, respectively, downgradient of the LNAPL plume. Well construction information and estimated capacities are presented in Table 2-2. Well Name Table 2-2. Water Production Wells, Vicinity of Kirtland AFB Solid Waste Management Units (SWMU) ST-106 and SS-111 Install Total Depth Screen Interval Casing Date (ft bgs) (ft bgs) (in) Est. Capacity (gpm) Burton 5 1991 1,170 550-1,150 20 3,000 Ridgecrest 5 1990 1,550 690-1,530 20 3,000 VA 1956 997 No data No data No data Kirtland 3 No data No data No data No data No data Kirtland 15 1996 1,511 700-1,430 18 2,500 Kirtland 16 1996 1,511 710-1,400 18 2,500 Construction workers who may be exposed to subsurface soils are also potential receptors. However, the existing KAFB digging permit clearance process provides notification and protection against inappropriate exposures to construction workers. Vapor intrusion may be a concern in any buildings located near the LNAPL release. An investigation of the potential for vapor intrusion was completed for two buildings overlying the LNAPL showed that risks associated with indoor air quality are acceptable. The report is currently in draft. Kirtland AFB June 2010 Groundwater Investigation Work Plan BFF 2-9
Page 1 and 2: KIRTLAND AIR FORCE BASE ALBUQUERQUE
Page 3 and 4: DOCUMENT CERTIFICATION REPORT DOCUM
Page 5 and 6: DOCUMENT CERTIFICATION THIS PAGE IN
Page 7 and 8: CONTENTS 3.3.7 Groundwater and LNAP
Page 9 and 10: FIGURES FIGURES 2-1 Site Location M
Page 11 and 12: ACRONYMS AND ABBREVIATIONS ACRONYMS
Page 13 and 14: THIS PAGE INTENTIONALLY LEFT BLANK
Page 15 and 16: SECTION 1 1.1 Objectives and Scope
Page 17 and 18: SECTION 2 2.1 Site Description 2. B
Page 19 and 20: SECTION 2 • From roughly 86 ft bg
Page 21 and 22: SECTION 2 2.4.2 Investigative Resul
Page 23: SECTION 2 previous sampling results
Page 27 and 28: SECTION 2 gpd. Investigating and re
Page 29 and 30: SECTION 3 3.2 Quality Assurance/Qua
Page 31 and 32: SECTION 3 being both an electrical
Page 33 and 34: SECTION 3 3.3.4 Groundwater Monitor
Page 35 and 36: SECTION 3 piezometers. Groundwater
Page 37 and 38: SECTION 4 association meetings are
Page 39 and 40: REFERENCES US Environmental Protect
Page 41 and 42: TABLES Table 2-1. Hydrostratigraphi
Page 43 and 44: TABLES Table 3-2 Proposed Installat
Page 45 and 46: TABLES Installation ID Installation
Page 51 and 52: Figures
Page 53 and 54: SAN METEO SAN PEDRO 1540886 1541386
Page 55 and 56: Source: CH2M HILL 2009 Figure 2-4
Page 57 and 58: Source: CH2M HILL 2009 Figure 2-6
Page 59 and 60: CONCEPTUAL SITE MODEL Figure 2-8 So
Page 61 and 62: SAN METEO SAN PEDRO 1540672 1541172
Page 63 and 64: Figure 3‐3 Typical Soil Vapor Mon
Page 65 and 66: Appendix A NMED Guidance: NMED TPH
Page 67 and 68: A TPH screening guideline was calcu
Page 69 and 70: potential indoor air impacts from s
Page 71 and 72: Appendix B Project Schedule
Page 73 and 74: Appendix C Preliminary Report Outli
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Appendix D Base-Wide Plans for Inve
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BASE-WIDE PLAN CONTENTS Section Pag
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BASE-WIDE PLAN FIGURES Section Page
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BASE-WIDE PLAN ACRONYMS AFB AFCEE C
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BASE-WIDE PLAN 1. INTRODUCTION Kirt
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BASE-WIDE PLAN 2. PROJECT MANAGEMEN
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BASE-WIDE PLAN Waste Management Pro
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BASE-WIDE PLAN 3. BASELINE ENVIRONM
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BASE-WIDE PLAN Figure 3-1. Kirtland
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BASE-WIDE PLAN Table 3-1. History o
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BASE-WIDE PLAN Figure 3-2. Location
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BASE-WIDE PLAN Figure 3-3. Geologic
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BASE-WIDE PLAN 3.1.3 Hydrogeology D
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BASE-WIDE PLAN the high nitrate lev
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BASE-WIDE PLAN Figure 3-4. Extent o
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BASE-WIDE PLAN REFERENCES Allen, H.
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APPENDIX A APPENDIX A Field Samplin
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APPENDIX A CONTENTS Section Page Ta
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APPENDIX A TABLES Table Page Table
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APPENDIX A ACRONYMS °C degrees Cel
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APPENDIX A 1. INTRODUCTION This Bas
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APPENDIX A 2. FIELD SAMPLING OBJECT
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APPENDIX A 3. DESIGN OF DATA COLLEC
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APPENDIX A Table 3-1. Activities As
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APPENDIX A probability. This techni
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APPENDIX A 4. SAMPLING EQUIPMENT AN
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APPENDIX A 4.3.3 Ambient Field Blan
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APPENDIX A 5. SAMPLE HANDLING AND A
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APPENDIX A 6. FIELD QA/QC PROGRAM T
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APPENDIX A 7. SITE MANAGEMENT AND R
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APPENDIX A The identity of each sam
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APPENDIX A REFERENCES EPA 1986. RCR
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APPENDIX B APPENDIX B Standard Oper
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APPENDIX B CONTENTS Section Page Ta
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APPENDIX B CONTENTS (Continued) Sec
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APPENDIX B TABLES Table B4.1-1. Qui
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APPENDIX B FIGURES Figure B1.1-1. T
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APPENDIX B ACRONYMS °C degrees Cel
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APPENDIX B SOP B1.1 Borehole and Sa
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APPENDIX B Gravely soils are identi
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APPENDIX B Stratification Stratific
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APPENDIX B Hardness The hardness of
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APPENDIX B Igneous rock classificat
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APPENDIX B Figure B1.1-1. Typical B
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APPENDIX B Figure B1.1-1. Typical B
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APPENDIX B Figure B1.1-2. The Unifi
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APPENDIX B SOP B1.2 Borehole Geophy
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APPENDIX B Waveforms obtained at ea
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APPENDIX B The borehole induction s
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APPENDIX B SOP B1.3 Monitoring Well
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APPENDIX B finished wells shall als
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APPENDIX B Figure B1.3-1. Overburde
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APPENDIX B Figure B1.3-2. Overburde
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APPENDIX B Figure B1.3-3. Double Ca
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APPENDIX B Figure B1.3-4. Double Ca
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APPENDIX B Chemical application The
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APPENDIX B Figure B1.4-1. Well Deve
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APPENDIX B Figure B1.4-1. Well Deve
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APPENDIX B Figure B1.5-1. Well Aban
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APPENDIX B SOP B1.6 Temporary Well-
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APPENDIX B SOP B1.7 Soil Gas Invest
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APPENDIX B If instrument blanks ind
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APPENDIX B SOP B1.8 Surficial Geoph
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APPENDIX B Relevant notes, remarks
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APPENDIX B Magnetic Surveys useful
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APPENDIX B SOP B1.9 Land Surveys A
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APPENDIX B SOP B1.10 Meteorological
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APPENDIX B SOP B1.11 Equipment Deco
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APPENDIX B Personal Protective Equi
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APPENDIX B SOP B2.1 Sediment Sampli
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APPENDIX B SOP B2.2 Surface Soil Sa
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APPENDIX B SOP B2.3 Subsurface Soil
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APPENDIX B Wear appropriate PPE as
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APPENDIX B the Classification of Ro
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APPENDIX B Using soil removed from
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APPENDIX B Collect and manage all w
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APPENDIX B SOP B2.4 Test Pit Sampli
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APPENDIX B SOP B2.5 Sample Homogeni
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APPENDIX B SOP B3.1 Photoionization
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APPENDIX B SOP B3.2 Methods for Usi
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APPENDIX B The rate of migration th
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APPENDIX B easily be penetrated wit
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APPENDIX B the identification or qu
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APPENDIX B SOP B3.3 Headspace Scree
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APPENDIX B the drawdown shall not e
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APPENDIX B Sample Collection Once r
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APPENDIX B Figure B4.1-1. Well Purg
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APPENDIX B Table B4.1-1. Quick Conv
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APPENDIX B SOP B4.2 Potable Water S
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APPENDIX B SOP B4.3 Surface Water S
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APPENDIX B SOP B4.4 Field Filtratio
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APPENDIX B SOP B5.1 pH The followin
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APPENDIX B SOP B5.2 Specific Conduc
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APPENDIX B SOP B5.3 Water Temperatu
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APPENDIX B SOP B5.4 Dissolved Oxyge
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APPENDIX B SOP B5.5 Oxidation-Reduc
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APPENDIX B SOP B5.6 Water Levels Wa
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APPENDIX B Figure B5.6-1. Groundwat
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APPENDIX B SOP B5.7 Aquifer Testing
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APPENDIX B Packer Testing Procedure
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APPENDIX B All measurements and obs
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APPENDIX B Figure B5.7-1a. Aquifer
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APPENDIX B Figure B5.7-1b. Aquifer
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APPENDIX B Figure B5.7-2. Pump Test
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APPENDIX B SOP B6.1 Drum Sampling F
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APPENDIX B SOP B6.2 Tank Sampling F
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APPENDIX B SOP B6.3 Wipe Sampling T
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APPENDIX B SOP B6.4 Concrete Sampli
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APPENDIX B SOP B6.5 Air Sampling/Ai
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APPENDIX B SOP B7.1 Approved Backgr
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APPENDIX B Table B7.1-1. Approved B
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APPENDIX B SOP B7.2 Use of NMED Soi
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APPENDIX B Table B7.2-1. NMED Soil
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APPENDIX B Table B7.2-1. NMED Soil
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APPENDIX B SOP B7.3 Radioactively-C
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APPENDIX B Material used by the Air
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APPENDIX C APPENDIX C Quality Assur
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APPENDIX C CONTENTS Section Page Ta
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APPENDIX C CONTENTS (Concluded) Sec
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APPENDIX C TABLES Table Page Table
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APPENDIX C ACRONYMS AFB AFCEE ASTM
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APPENDIX C 1. INTRODUCTION This Bas
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APPENDIX C 2. PROJECT DESCRIPTION 2
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APPENDIX C 3. PROJECT ORGANIZATION
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APPENDIX C 2.7 Safety Professional
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APPENDIX C 4. QUALITY ASSURANCE OBJ
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APPENDIX C 4.1.4 Accuracy Accuracy
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APPENDIX C procedures that may resu
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APPENDIX C 5. FIELD INVESTIGATION P
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APPENDIX C Table 5-1. Sample Requir
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APPENDIX C Table 5-2. Sample Requir
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APPENDIX C 6. SAMPLE CUSTODY AND RE
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COMP GRAB PRESERVATIVE PRESERVATIVE
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APPENDIX C sections. The data packa
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APPENDIX C 7. CALIBRATION PROCEDURE
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APPENDIX C Geophysical surveying eq
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APPENDIX C 8. ANALYTICAL PROCEDURES
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APPENDIX C 9. INTERNAL QUALITY CONT
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APPENDIX C basis and at a frequency
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APPENDIX C 10. DATA VALIDATION, RED
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APPENDIX C Numerical value and unit
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APPENDIX C 11. PERFORMANCE AND SYST
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APPENDIX C 12. PREVENTIVE MAINTENAN
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APPENDIX C 13. DATA ASSESSMENT The
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APPENDIX C An independent team (ind
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APPENDIX C 14. CORRECTIVE ACTION Co
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APPENDIX C Figure 14-1. Nonconforma
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APPENDIX C 2.44 Data Validation and
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APPENDIX C 15. QUALITY ASSURANCE RE
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APPENDIX C Discussion of qualified
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APPENDIX C REFERENCES Air Force Cen
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APPENDIX D APPENDIX D Data Manageme
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APPENDIX D CONTENTS Contents Page T
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APPENDIX D TABLES Tables Page Table
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APPENDIX D ACRONYMS AFB AFCEE ASTM
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APPENDIX D 1. INTRODUCTION 1.1 Purp
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APPENDIX D 2. DATA QUALITY OBJECTIV
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APPENDIX D 3. PARTICIPANTS AND RESP
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APPENDIX D Table 3-1. Participants
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APPENDIX D 4. DATA MANAGEMENT SYSTE
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APPENDIX D The purpose of data revi
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APPENDIX D Compound identification
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APPENDIX D Sample ID Sample Depth (
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APPENDIX D LDI SLXI WCI GWD SAMP CA
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APPENDIX D REFERENCES AFCEE 1993. H
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APPENDIX E APPENDIX E Waste Managem
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APPENDIX E CONTENTS Section Page Ta
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APPENDIX E TABLES Table Page Table
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APPENDIX E ACRONYMS AFB AOC ACM ARA
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APPENDIX E 1. INTRODUCTION This doc
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APPENDIX E Not excluded from regula
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APPENDIX E ― Maintain or construc
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APPENDIX E 2. REGULATORY REQUIREMEN
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APPENDIX E EPA Hazardous Waste Code
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APPENDIX E 3. WASTE MANAGEMENT CONT
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APPENDIX E Special wastes (PCS and
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APPENDIX E hazardous waste will imm
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APPENDIX E Figure 3-1. Typical Haza
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APPENDIX E 4. SUMMARY OF EXPECTED I
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APPENDIX E Table 4-1. Waste Managem
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APPENDIX E which allows waste to be
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APPENDIX E 5. HAZARDOUS WASTE GENER
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APPENDIX E 5.2.4.3 Radioactive Wast
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APPENDIX E 5.3.4.1 Special Waste Al
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APPENDIX E ― Waste profile sheets
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APPENDIX E copies of manifests from
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APPENDIX E REFERENCES USAF 1996. Ra
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APPENDIX F APPENDIX F Base-wide Hea
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APPENDIX F CONTENTS Table Page Acro
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APPENDIX F CONTENTS (Concluded) Sec
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APPENDIX F ACRONYMS ACGIH AFB AHA A
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APPENDIX F 1. INTRODUCTION 1.1 Purp
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APPENDIX F 2. PROJECT ORGANIZATION
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APPENDIX F Ensure that Contractor e
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APPENDIX F Provide updated document
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APPENDIX F 3. SITE HISTORY AND DESC
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APPENDIX F 4. POTENTIAL HAZARDS The
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APPENDIX F symptoms of heat stress,
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APPENDIX F irrational or stuporous
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APPENDIX F pounds. Objects heavier
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APPENDIX F All circuit breaker pane
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APPENDIX F SHSS will identify these
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APPENDIX F When using a hammer wear
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APPENDIX F All unattended boreholes
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APPENDIX F Minimize shock loading o
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APPENDIX F Apply an adequate amount
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APPENDIX F All personnel involved i
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APPENDIX F To avoid battery explosi
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APPENDIX F distances that heavier e
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APPENDIX F as discussed here refer
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APPENDIX F 5. ACTIVITY HAZARD ANALY
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APPENDIX F 6. PERSONAL PROTECTIVE E
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APPENDIX F Coveralls (outer), chemi
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APPENDIX F 7. AIR, NOISE, AND OTHER
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APPENDIX F 8. SITE CONTROL The PM,
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APPENDIX F 8.2.3 Equipment Decontam
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APPENDIX F 9. MEDICAL SURVEILLANCE
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APPENDIX F 10. SAFETY CONSIDERATION
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APPENDIX F 10.2.2 Housekeeping Clea
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APPENDIX F Shut off and bleed down
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APPENDIX F Protect your hands and f
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APPENDIX F 10.2.16 Electricity Keep
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APPENDIX F 11. DISPOSAL PROCEDURES
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APPENDIX F 12. EMERGENCY RESPONSE P
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APPENDIX F 12.5.3 Medical Emergency
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APPENDIX F safe environment. In the
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APPENDIX F Each SHSP may specify ad
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APPENDIX F 13. TRAINING In accordan
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APPENDIX F 14. LOGS, REPORTS, AND R
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APPENDIX F 15. FIELD PERSONNEL REVI
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APPENDIX F 16. REFERENCES Occupatio
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APPENDIX G APPENDIX G Construction
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APPENDIX G CONTENTS Section Page 1.
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APPENDIX G 1. INTRODUCTION TO CONST
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APPENDIX H APPENDIX H Permitting Pl
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APPENDIX H CONTENTS Section Page 1.
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APPENDIX H 1. PERMIT CONSIDERATIONS
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APPENDIX H Permit Type Agency Conta
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APPENDIX H Permit Type Agency Conta
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APPENDIX I APPENDIX I Community Rel
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APPENDIX J APPENDIX J Land Use Plan
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APPENDIX J APPENDIX K Document Cont
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