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Preven ng Columbia/Potomac Aquifer Cross Contamina on in the Decommissioning of an In-Ground Frozen Earth Propane Storage Facility, Delaware City ReĮnery, Delaware Smith, Chad A., and Jengo, John W. , MWH Americas, Inc. Malvern, Pennsylvania In-Ground Frozen Earth Propane Storage Proprietary design developed by Phillips Petroleum Co. One of two covered subterranean propane storage caverns in US; commissioned in 1966 Stored propane/propylene (C3) at -45°F, atmospheric condiƟons (0.3 psi) 165 feet in diameter and 128 feet deep, with capacity of about 495,000 barrels Cavern wall integrity accomplished by circulaƟon of liquid propane through three concentric rings of 250 verƟcal “freeze” pipes. FugiƟve emissions from cavern triggered ConciliaƟon Order (CO) from DNREC in 2008. CO required the FES be closed in a safe and environmentally sound method. Hydrogeology Geologic Seƫng Cavern was excavated through Columbia, the remnant thickness of the Merchantville, and about 45 feet of upper Potomac sand and interlaminated sand and silt beds. InvesƟgaƟve programs conducted throughout the reĮnery provided extensive knowledge of subsurface condiƟons underlying the FES facility. Columbia FormaƟon (Qcl): Pleistocene-age Ňuvial Įne- to coarse-grained, poorly-sorted quartz sand with silt and gravel. Southward groundwater Ňow Columbia Fm and Potomac Fm aquifers are hydraulically connected to the west of FES. Groundwater of the unconĮned Columbia Fm aquifer and upper sands of Potomac Fm aquifer has been impacted by historical reĮnery operaƟons, primarily petroleum hydrocarbons (benzene, naphthalene) and addiƟve contaminants (methyl-tert-butyl-ether [MTBE]). Decommissioning Concerns Cavern would represent a signiĮcant “open channel” connecƟon between the Columbia and Potomac Fms once the FES returns to ambient ground temperatures. 250 freeze pipes penetrate deep (225 feet) into Potomac Fm and could create conduit for impacted groundwater. ConĮrming the decommissioning does not degrade water quality. PROJECT OBJECTIVES 1. Re-establish a low permeability horizon that will separate the Columbia Fm from the Potomac Fm 2. Properly abandon verƟcal freeze pipes to seal oī potenƟal conduit between Columbia and Potomac Fms 3. Implement groundwater monitoring to develop baseline groundwater condiƟons and monitor groundwater quality before, during, and aŌer decommissioning acƟviƟes Merchantville FormaƟon (Kmv): Late Cretaceous-age (Early Campanian) shallow marine silt to clayey silt with intervals of Įne-grained sandy silty clay, silty clay and Įne-grained sand; locally a conĮning layer. Potomac FormaƟon (Kpt) – Early (ApƟan, Albian) and Late (Cenomanian) Cretaceous-age succession of non-marine (anastomosing river systems and wet Ňoodplains) silts, clays, and sands; Upper and lower sandy, aquifer-prone intervals provide much of the drinking water for this region of Delaware. CAVERN SchemaƟc Cross-SecƟon of Cavern ConstrucƟon FREEZE PIPES FROZEN EARTH FREEZE PIPES BACKFILLING THE CAVERN Re-establishing Aquifer /ƐŽůĂƟŽŶ Grout SpeciĮcaƟons Hydraulic ConducƟvity less than 1 x 10 -3 cm/sec UnconĮned Compressive Strength >25 psi 60 feet thick, from cavern boƩom to 68 Ō bgs Material and leachate cerƟĮed clean: below Delaware Uniform Risk-Based RemediaƟon Standard (DURS) for ProtecƟon of Human Health Total of 42,000 CY MulƟ-Layer Grout Slurry Plug and Sand BacŬĮll Method selected as most protecƟve and cost-eīecƟve bacŬĮll method Grout TesƟng Three mixtures of varying amounts of sand/gravel, cement, bentonite, water Sand included three DMSA sands (A7, L8, Y7) and one oī-site sand (C) Brackish water from reĮnery-supplied Įre water system (from Delaware River) used in mixes Samples frozen for 14 days at 0°F/-17°C, thawed and tested Compressive Strength (D2166), Permeability (D5084), environmental analyƟcal tesƟng TesƟng Results On-site sand mixes did not meet speciĮcaƟons, requiring use of oī-site sand mixes Frozen samples exhibited lower strengths and increased hydraulic conducƟvity, but met speciĮcaƟons AnalyƟcal results for VOCs, SVOCs, PesƟcides, PCBs, and Metals below DURS Brackish water suitable for use in mixes Type 1 mix with Oī-site sand selected for grout BeneĮcial Re-use of On-Site Dredge Sand Eliminated potenƟal safety issues and road degradaƟon caused by 8,300 roundtrips of trucks hauling on Delaware roads EsƟmated 40,000 gallons of diesel fuel conserved Saved approximately $150,000 compared with purchase of oī-site sand Grout emplaced via pumping into crane-supported tremie pipe. On-site batch plant provided 42,000 CY, emplaced in 50 days Measured depths to grout daily Grout strengths and hydraulic conducƟvity consistent throughout emplacement Strengths and hydraulic conducƟvity met speciĮcaƟons Grout Emplacement Sand BacŬĮll SpeciĮcaƟons ParƟcle size >75% Sand Material and leachate cerƟĮed clean: below Delaware Uniform Risk-Based RemediaƟon Standard (DURS) for ProtecƟon of Human Health Total of 60,000 CY Sand Source EvaluaƟon Oī-site source: Borrow pits in Maryland/Southern Delaware On-site source: nearby Dredge Material Storage Area (DMSA) Detailed invesƟgaƟon of DMSA determined 80,000 CY was sand Some naturally occurring arsenic; VOCs, SVOCs, PesƟcides, PCBs, and Metals below DURS On-site DMSA dredge sand selected; approved by DNREC for use as backĮll Sand Emplacement 70,000 CY excavated during dry summer months and stockpiled close to cavern Field QC conĮrmed material >75% Įne to medium sand; 78% of tests were > 90% sand Emplaced sand via direct loading through hatches cut in dome 60,000 CY sand emplaced over ~65 days On-site computer-controlled grout plant assembled to provide 1,000 CY of grout per day Delivery of grout into cavern via crane- supported tremie pipe inserted through dome manhole Final grout plug surface at 68 feet below ground surface Sand backĮll piles within cavern Sand pile on south side of cavern (leŌ); Columbia Fm bedding visible on cavern walls (right) ExcavaƟon of sand from DMSA Stockpile of 70,000 CY of sand excavated from DMSA; located 1,500 Ō from FES Cavern Field tesƟng grout strength Direct loading of sand into cavern Sand content distribuƟon within 200-acre Dredge Material Storage Area. Red circles indicate on-site sand used in grout mix tesƟng Chronologic progression of grout emplacement and Įnal as-built grout elevaƟons ABANDONING THE FREEZE PIPES ProteĐƟŶŐ the Potomac FormĂƟŽŶ Aquifer 253 verƟcal pipes in three concentric rings 150 to 225 feet deep Buried under earthen berm 1-inch diameter inner pipe within 4.5-inch diameter outer pipe Liquid propane supplied within 1-inch pipe and propane vapor returns through the annular space of the 4.5-inch pipe UƟlized exisƟng 1-inch pipe as a tremie pipe to Įll pipe from boƩom up Portland cement grout placed in one-conƟnuous operaƟon unƟl grout overŇowed at surface Freeze Pipe Abandonment “Delaware RegulaƟons Governing the ConstrucƟon and Use of Wells” SecƟon 9.0 – Well Abandonment ObjecƟve to seal each pipe “to limit its potenƟal as a pathway for verƟcal migraƟon of Ňuids between diīerent aquifers.” Concrete, Portland cement grout, sodium- based bentonite clay grout, or combinaƟons of these materials will be used to abandon the pipes. Portland cement grout and sodium-based bentonite clay grout shall meet the weight and composiƟon requirements of SecƟon 4.07(J)(1) and (2) of the Well RegulaƟons. All pipes will be Įlled with the appropriate sealing materials starƟng from the boƩom of the pipe upward using the tremie grouƟng technique to ensure proper displacement of water or air in the pipe. When Portland cement grout or concrete is used as a sealing material, it shall be placed in one conƟnuous operaƟon. The pipes will be Įlled unƟl the sealing material overŇowing the pipe is of the same consistency and density as the sealing material being pumped into the pipe. 1. Array of freeze pipes aŌer removal of earthen berm 6. Portland cement returning to surface through 2-inch vapor return port during pumping 5. Grout hose connected to 1-inch inner pipe 4. Portland cement delivered by truck to drill rig 3. Array of freeze pipes awaiƟng abandonment 2. Cuƫng of 4.5-inch pipe and liŌing to expose 1-inch inner pipe 7. Array of abandoned freeze pipes Freeze pipe diagram showing circulaƟon of propane during refrigeraƟon Used same circulaƟon design to abandon freeze pipes with grout Layout of three concentric rings of freeze pipes around cavern Freeze pipes 8. Cuƫng abandoned pipes with shear aƩachment GROUNDWATER MONITORING DocumenƟŶŐ the Decommissioning New Columbia Fm Wells Document groundwater quality of the Columbia and Potomac formaƟons in the vicinity of the FES before, during, and aŌer the FES closure acƟviƟes to determine if: Historical petroleum hydrocarbon impacts are present in the vicinity of the FES Decommissioning acƟviƟes signiĮcantly alter groundwater quality Groundwater near the FES is impacted with propane Monitoring ObjecƟves Groundwater InvesƟgaƟon Installed three new Columbia Fm wells Installed one new Potomac Fm well Sampling events: Prior to Decommissioning (Dec 2009) During Decommissioning (Nov 2010) AŌer Decommissioning (Dec 2011) New Potomac Fm Well Hydrogeologic CondiƟons Groundwater Ňows southwest towards the FES, and conƟnues to the south-southwest Frozen soil and groundwater causing groundwater to Ňow around the FES cavern Downward verƟcal hydraulic gradient – 0.012 Ō/Ō Drilling MW3 into Columbia Fm aquifer using Roto-sonic drilling methods Installing 6-inch isolaƟon casing at MW4 (Potomac well) MWH geologist logging soils from MW1 Groundwater Results Benzene and MTBE concentraƟons are consistent with nearby wells related to the pre-exisƟng plume Benzene and MTBE did not change signiĮcantly during or aŌer the decommissioning Propane is present in groundwater at relaƟvely low concentraƟons, except immediately downgradient (MW3) Although main source of propane has been removed, the conƟnued presence of propane in groundwater is aƩributed to: Thawing of the frozen soil around the cavern releasing small amounts of entrapped propane Depressed groundwater temperatures around the cavern hindering the volaƟlizaƟon of propane OBJECTIVES ACCOMPLISHED Sealing oī the Potomac and Merchantville Fms provided protecƟon from potenƟal future liƟgaƟon regarding the historically impacted groundwater Abandoning the freeze pipes prevented potenƟal future conduit for impacted groundwater to deeper porƟons of the Potomac Fm aquifer Groundwater monitoring demonstrated that the decommissioning did not adversely aīect groundwater Historical Source Areas Impacted Groundwater (MTBE, Benzene) ExisƟng Columbia Fm Well Post-closure condiƟon of former FES cavern aŌer Įnal backĮlling and grading

Preven ng Columbia/Potomac Aquifer Cross Contamina on in the … · 2012-12-11 · Preven ng Columbia/Potomac Aquifer Cross Contamina on in the Decommissioning of an In-Ground Frozen

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Page 1: Preven ng Columbia/Potomac Aquifer Cross Contamina on in the … · 2012-12-11 · Preven ng Columbia/Potomac Aquifer Cross Contamina on in the Decommissioning of an In-Ground Frozen

Preven ng Columbia/Potomac Aquifer Cross Contamina on in the Decommissioning of an In-Ground Frozen Earth Propane Storage Facility, Delaware City Re nery, DelawareSmith, Chad A., and Jengo, John W. , MWH Americas, Inc. Malvern, Pennsylvania

In-Ground Frozen Earth Propane Storage Proprietary design developed by Phillips Petroleum Co.

One of two covered subterranean propane storage caverns in US; commissioned in 1966

Stored propane/propylene (C3) at -45°F, atmospheric condi ons (0.3 psi)

165 feet in diameter and 128 feet deep, with capacity of about 495,000 barrels

Cavern wall integrity accomplished by circula on of liquid propane through three concentric rings of 250 ver cal “freeze” pipes.

Fugi ve emissions from cavern triggered Concilia on Order (CO) from DNREC in 2008. CO required the FES be closed in a safe and environmentally sound method.

Hydrogeology

Geologic Se ng

Cavern was excavated through Columbia, the remnant thickness of the Merchantville, and about 45 feet of upper Potomac sand and interlaminated sand and silt beds.

Inves ga ve programs conducted throughout the re nery provided extensive knowledge of subsurface condi ons underlying the FES facility. Columbia Forma on (Qcl): Pleistocene-age

uvial ne- to coarse-grained, poorly-sorted quartz sand with silt and gravel.

Southward groundwater ow

Columbia Fm and Potomac Fm aquifers are hydraulically connected to the west of FES.

Groundwater of the uncon ned Columbia Fm aquifer and upper sands of Potomac Fm aquifer has been impacted by historical re nery opera ons, primarily petroleum hydrocarbons (benzene, naphthalene) and addi ve contaminants (methyl-tert-butyl-ether [MTBE]).

Decommissioning Concerns Cavern would represent a signi cant “open channel” connec on between the Columbia and Potomac Fms once the FES returns to ambient ground temperatures.

250 freeze pipes penetrate deep (225 feet) into Potomac Fm and could create conduit for impacted groundwater.

Con rming the decommissioning does not degrade water quality.

PROJECT OBJECTIVES 1. Re-establish a low permeability horizon that will separate the Columbia Fm from the Potomac Fm

2. Properly abandon ver cal freeze pipes to seal o poten al conduit between Columbia and Potomac Fms

3. Implement groundwater monitoring to develop baseline groundwater condi ons and monitor groundwater quality before, during, and a er decommissioning ac vi es

Merchantville Forma on (Kmv): Late Cretaceous-age (Early Campanian) shallow marine silt to clayey silt with intervals of ne-grained sandy silty clay, silty clay and

ne-grained sand; locally a con ning layer.

Potomac Forma on (Kpt) – Early (Ap an, Albian) and Late (Cenomanian) Cretaceous-age succession of non-marine (anastomosing river systems and wet oodplains) silts, clays, and sands; Upper and lower sandy, aquifer-prone intervals provide much of the drinking water for this region of Delaware.

CAVERN

Schema c Cross-Sec on of Cavern Construc on

FREEZE PIPES

FROZEN EARTH

FREEZE PIPES

BACKFILLING THE CAVERN Re-establishing Aquifer

Grout Speci ca ons Hydraulic Conduc vity less than 1 x 10-3 cm/sec

Uncon ned Compressive Strength >25 psi

60 feet thick, from cavern bo om to 68 bgs

Material and leachate cer ed clean: below Delaware Uniform Risk-Based Remedia on Standard (DURS) for Protec on of Human Health

Total of 42,000 CY

Mul -Layer Grout Slurry Plug and Sand Bac ll Method selected as most

protec ve and cost-e ec ve bac ll method

Grout Tes ng Three mixtures of varying amounts of sand/gravel, cement, bentonite, water

Sand included three DMSA sands (A7, L8, Y7) and one o -site sand (C)

Brackish water from re nery-supplied re water system (from Delaware River) used in mixes

Samples frozen for 14 days at 0°F/-17°C, thawed and tested

Compressive Strength (D2166), Permeability (D5084), environmental analy cal tes ng

Tes ng Results On-site sand mixes did not meet speci ca ons, requiring use of o -site sand mixes Frozen samples exhibited lower strengths and increased hydraulic conduc vity, but met speci ca ons Analy cal results for VOCs, SVOCs, Pes cides, PCBs, and Metals below DURS Brackish water suitable for use in mixes Type 1 mix with O -site sand selected for grout

Bene cial Re-use of On-Site Dredge Sand Eliminated poten al safety issues and road degrada on caused by 8,300 roundtrips of trucks hauling on Delaware roads Es mated 40,000 gallons of diesel fuel conserved Saved approximately $150,000 compared with purchase of o -site sand

Grout emplaced via pumping into crane-supported tremie pipe.

On-site batch plant provided 42,000 CY, emplaced in 50 days

Measured depths to grout daily

Grout strengths and hydraulic conduc vity consistent throughout emplacement

Strengths and hydraulic conduc vity met speci ca ons

Grout Emplacement

Sand Bac ll Speci ca ons Par cle size >75% Sand

Material and leachate cer ed clean: below Delaware Uniform Risk-Based Remedia on Standard (DURS) for Protec on of Human Health

Total of 60,000 CY

Sand Source Evalua on O -site source: Borrow pits in Maryland/Southern Delaware On-site source: nearby Dredge Material Storage Area (DMSA)

Detailed inves ga on of DMSA determined 80,000 CY was sand Some naturally occurring arsenic; VOCs, SVOCs, Pes cides, PCBs, and Metals below DURS

On-site DMSA dredge sand selected; approved by DNREC for use as back ll

Sand Emplacement 70,000 CY excavated during dry summer months and stockpiled close to cavern

Field QC con rmed material >75% ne to medium sand; 78% of tests were > 90% sand

Emplaced sand via direct loading through hatches cut in dome

60,000 CY sand emplaced over ~65 days

On-site computer-controlled grout plant assembled to provide 1,000 CY of grout per day

Delivery of grout into cavern via crane- supported tremie pipe inserted through dome manhole

Final grout plug surface at 68 feet below ground surface

Sand back ll piles within cavern Sand pile on south side of cavern (le ); Columbia Fm bedding visible on cavern walls (right)

Excava on of sand from DMSA

Stockpile of 70,000 CY of sand excavated from DMSA; located 1,500 from FES Cavern

Field tes ng grout strength

Direct loading of sand into cavern

Sand content distribu on within 200-acre Dredge Material Storage Area. Red circles indicate on-site sand used in grout mix tes ng

Chronologic progression of grout emplacement and nal as-built grout eleva ons

ABANDONING THE FREEZE PIPES Prote the Potomac Form Aquifer

253 ver cal pipes in three concentric rings

150 to 225 feet deep

Buried under earthen berm

1-inch diameter inner pipe within 4.5-inch diameter outer pipe

Liquid propane supplied within 1-inch pipe and propane vapor returns through the annular space of the 4.5-inch pipe

U lized exis ng 1-inch pipe as a tremie pipe to ll pipe from bo om up

Portland cement grout placed in one-con nuous opera on un l grout over owed at surface

Freeze Pipe Abandonment “Delaware Regula ons Governing the Construc on and Use of Wells”

Sec on 9.0 – Well Abandonment Objec ve to seal each pipe “to limit its poten al as a pathway for ver cal migra on of uids between di erent aquifers.”

Concrete, Portland cement grout, sodium-based bentonite clay grout, or combina ons of these materials will be used to abandon the pipes.

Portland cement grout and sodium-based bentonite clay grout shall meet the weight and composi on requirements of Sec on 4.07(J)(1) and (2) of the Well Regula ons.

All pipes will be lled with the appropriate sealing materials star ng from the bo om of the pipe upward using the tremie grou ng technique to ensure proper displacement of water or air in the pipe.

When Portland cement grout or concrete is used as a sealing material, it shall be placed in one con nuous opera on.

The pipes will be lled un l the sealing material over owing the pipe is of the same consistency and density as the sealing material being pumped into the pipe.

1. Array of freeze pipes a er removal of earthen berm

6. Portland cement returning to surface through 2-inch vapor return port during pumping

5. Grout hose connected to 1-inch inner pipe

4. Portland cement delivered by truck to drill rig

3. Array of freeze pipes awai ng abandonment

2. Cu ng of 4.5-inch pipe and li ing to expose 1-inch inner pipe

7. Array of abandoned freeze pipes

Freeze pipe diagram showing circula on of propane during refrigera on

Used same circula on design to abandon freeze pipes with grout

Layout of three concentric rings of freeze pipes around cavern

Freeze pipes

8. Cu ng abandoned pipes with shear a achment

GROUNDWATER MONITORING Documen the Decommissioning

New Columbia Fm Wells

Document groundwater quality of the Columbia and Potomac forma ons in the vicinity of the FES before, during, and a er the FES closure ac vi es to determine if:

Historical petroleum hydrocarbon impacts are present in the vicinity of the FES Decommissioning ac vi es signi cantly alter groundwater quality Groundwater near the FES is impacted with propane

Monitoring Objec ves

Groundwater Inves ga on Installed three new Columbia Fm wells

Installed one new Potomac Fm well

Sampling events:

Prior to Decommissioning (Dec 2009)

During Decommissioning (Nov 2010)

A er Decommissioning (Dec 2011)

New Potomac Fm Well

Hydrogeologic Condi ons Groundwater ows southwest towards the FES, and con nues to the south-southwest

Frozen soil and groundwater causing groundwater to ow around the FES cavern

Downward ver cal hydraulic gradient – 0.012 /

Drilling MW3 into Columbia Fm aquifer using Roto-sonic drilling methods

Installing 6-inch isola on casing at MW4 (Potomac well)

MWH geologist logging soils from MW1

Groundwater Results Benzene and MTBE concentra ons are consistent with nearby wells related to the pre-exis ng plume Benzene and MTBE did not change signi cantly during or a er the decommissioning Propane is present in groundwater at rela vely low concentra ons, except immediately downgradient (MW3) Although main source of propane has been removed, the con nued presence of propane in groundwater is a ributed to:

Thawing of the frozen soil around the cavern releasing small amounts of entrapped propane

Depressed groundwater temperatures around the cavern hindering the vola liza on of propane

OBJECTIVES ACCOMPLISHED

Sealing o the Potomac and Merchantville Fms provided protec on from poten al future li ga on regarding the historically impacted groundwater Abandoning the freeze pipes prevented poten al future conduit for impacted groundwater to deeper por ons of the Potomac Fm aquifer Groundwater monitoring demonstrated that the decommissioning did not adversely a ect groundwater

Historical Source Areas

Impacted Groundwater (MTBE, Benzene)

Exis ng Columbia Fm Well

Post-closure condi on of former FES cavern a er nal back lling and grading