MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team [email protected].

23
MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team [email protected]

Transcript of MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team [email protected].

Page 1: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

MARCELLUS OVERVIEW

Amy Bergdale

US EPA, R3, OMA, Freshwater Biology Team

[email protected]

Page 2: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Source TCF

Barnett Shale - TX 2.1 - 30

Anadarko Basin – TX to KS 100

Haynesville Shale – Gulf Coast 250

Prudhoe Bay – North AK 28

Marcellus 168 - 516

SOURCES of GAS

Asalouyeh, South Pars Gas Field- Iran 500

Urengoy gas field- Russia 385

Iolotan gas field - Turkmenistan 264

Page 3: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

ANNUAL U.S. Production

2008: 23,241,512 MCF

http://www.eia.doe.gov/basics/naturalgas_basics.html

Page 4: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.
Page 5: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Vertical vs. Horizontal Drilling

Page 6: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Land Use Alteration & Infrastructure

www.ltresources.com.au

•Access Roads

•Well pads

•Transport vehicles

•Compression stations

•Cleaning stations

•Pipelines

Page 7: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Process•WATER

•Ground, surface,

municipal

•PROPPANTS

•Silica sand, bauxite

•ADDITIVES

•Surfactants, biocides, friction reducers, acids, oxygen stabilizers

•SHALE AND OVERBURDEN COMPOSITION

Page 8: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Characterizing the Waste

• Surfactants• Organics• TDS

– 30,000 to 230,000+ mg/l • Chlorides

– 15,000 to 110,000+ mg/l• Metals

– Barium, Strontium– Selenium

• TENORM– Radium 226, 228– Gross alpha, beta– Uranium– Radon

Page 9: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

TDS - 70,334mg/LCI - 37,460mg/L

TDS – N/ACI – 30,000 mg/L

TDS – 211,000 mg/LCI – 102,000 mg/L

Gross alpha – 960 pCi/L

TDS – 217,000 mg/LCI – 107,000 mg/L

Gross alpha – 3420 pCi/L

TDS – 132,000 mg/LCI – 121,000 mg/L

Gross alpha – 3330 pCi/L

Page 10: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Staged Flowback of Marcellus Well - WV

0

20,000

40,000

60,000

80,000

100,000

120,000

140,000

Day 1 Day 5 Day 10 Day 20 Day 30

mg

/L

0

100,000

200,000

300,000

400,000

500,000

600,000

700,000

mg

/L

Chloride Total Dissolved Solids Specific Conductivity

Characterizing the Waste

Page 11: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Characterizing the Waste

• Surfactants• Organics• TDS

– 30,000 to 230,000+ mg/l • Chlorides

– 15,000 to 110,000+ mg/l• Metals

– Barium, Strontium– Selenium

• TENORM– Radium 226, 228– Gross alpha, beta– Uranium– Radon

Page 13: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Chloride Brine Data from Western PA

0

20000

40000

60000

80000

100000

120000

mg/

L

Avg 65600 mg/L

Characterizing the Waste in PA

Page 14: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Calculating Receiving Water Concentrations Under Critical Conditions for Brine Treatment

• Criterion for protection of aquatic life from chronic effects from Pollutant X (in our case we are using Chloride as our pollutant of concern)

Upstream

(Qs, Cs)

Downstream

(Qr, Cr)

Discharge (Qd, Cd)

Page 15: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Determining a Critical Value (Cr)

Upstream

(Qs, Cs)

Downstream

(Qr, Cr)

Discharge (Qd, Cd)

Criterion for protection of aquatic life from chronic effects:

Qs = Critical stream flow (7Q10) for chronic criterion

Qd = Critical effluent flow from discharge flow data

Qr = Sum of critical stream flow and critical effluent flow

Cs = Critical upstream pollutant concentration

Cd = Critical effluent pollutant concentration

Cr = QsCs + QdCd

Qr

Page 16: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Determining a Critical Value (Cr)

Upstream

(Qs, Cs)

Downstream

(Qr, Cr)

Discharge (Qd, Cd)

•Ohio River, River Mile 40, U.S. Chester, WV

•Background chloride 100mg/L

•Large 100mgd (155cfs) Treatment Facility

•7Q10: 2,060cfs

•Max observed is 109000mg/L of 16 samples

•Cd = 109000 * 2.5 = 272,500mg/L (assuming 99th percentile, default CV of 0.6)

Cr = QsCs + QdCd

Qr

= 19162 mg/L >382 mg/L

Conclusion: The discharge would cause, have the reasonable potential to cause, or contribute to an excursion of the recalculated National Aquatic Life Criteria

Page 17: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Determining a Critical Value (Cr)

Upstream

(Qs, Cs)

Downstream

(Qr, Cr)

Discharge (Qd, Cd)

•S.F. Tenmile

•Background chloride of 28.5mg/L

•Large 0.8mgd (1.23cfs) Treatment Facility

•7Q10: 3.75cfs

•Max observed is 109000mg/L of 16 samples

•Cd = 109000 * 2.5 = 272,500mg/L (assuming 99th percentile, default CV of 0.6)

Cr = QsCs + QdCd

Qr

= 67,326 mg/L >382 mg/L

Conclusion: The discharge would cause, have the reasonable potential to cause, or contribute to an excursion of the recalculated National Aquatic Life Criteria

Page 18: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

What if diluted?

VS.

Ohio River Receiving

Cr = 19162 mg/L > 382 mg/L recalculated National Aquatic Life Criteria

10% = 1916 mg/L

5% = 958 mg/L

1% = 192 mg/L

0.5% = 96 mg/L

S. F. Tenmile Receiving

Cr = 67,326 mg/L > 382 mg/L recalculated National Aquatic Life Criteria

10% = 6733 mg/L

5% = 3366 mg/L

1% = 673 mg/L

0.5% = 337 mg/L < 382 mg/L< 382 mg/L

Page 19: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Characterizing the Waste

• Surfactants• Organics• TDS

– 30,000 to 230,000+ mg/l • Chlorides

– 15,000 to 110,000+ mg/l• Metals

– Barium, Strontium– Selenium

• TENORM– Radium 226, 228– Gross alpha, beta– Uranium– Radon

Page 20: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Stage Flowback from Marcellus well - WV

0

500

1000

1500

2000

2500

3000

3500

Day 1 Day 5 Day 10 Day 20

piC

/L

Gross Alpha Radioactivity Gross Beta Radioactivity

Radium 226 Radium 228

Characterizing the Waste

Page 21: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Contaminant MCL (year promulgated) Source Health Effect

Combined radium-226/-228 5 pCi/L (1976)Naturally occurs in some

drinking water sources.

Some people who drink water containing radium –226 or -228 in excess of the MCL over many years may have an increased risk of getting cancer.

(Adjusted) Gross Alpha15 pCi/L (not including radon

or uranium) (1976)Naturally occurs in some

drinking water sources.

Some people who drink water containing alpha emitters in excess of the MCL over many years may have an increased risk of getting cancer.

Beta Particle and Photon Radioactivity

4 mrem/year (look-up table) (1976)

May occur due to contamination from facilities using or producing radioactive materials.

Some people who drink water containing beta and photon emitters in excess of the MCL over many years may have an increased risk of getting cancer.

Uranium 30 µg/L (2000)Naturally occurs in some

drinking water sources.

Exposure to uranium in drinking water may result in toxic effects to the kidney. Some people who drink water containing alpha emitters in excess of the MCL over many years may have an increased risk of getting cancer.

Radionuclide MCLs

960, 3420, 12500 pCi/L

299, 1005, 12.49 pCI/L

Page 22: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Reasonable Potential for Radionuclides??

Radium 226+228• Ohio River, 2060cfs• Max observed, 1005

pCi/L * 5.6 = 5628 pCi/L• = 398 pCi/L

Radium 226+228• S.F. Tenmile, 3.75 cfs

• = 1390 pCi/L

Gross alpha• Ohio River, 2060cfs• Max observed, 12500

pCi/L * 5.6 = 70000 pCi/L• = 4898 pCi/L

Gross alpha• S.F. Tenmile, 3.75cfs

• = 17289 pCi/L

5 pCi/L

15 pCi/L

Page 23: MARCELLUS OVERVIEW Amy Bergdale US EPA, R3, OMA, Freshwater Biology Team Bergdale.Amy@epa.gov.

Where are we at????Has the WASTE been characterized?

How is the WASTE being treated?

What are the characteristics of the EFFLUENT?

What are the characteristics of your RECEIVING water?

Are you PROTECTING the AQUATIC LIFE USE?