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Climate Change and
Hydraulic Fracturing
Proppants:
Calculating the Carbon Dioxide
Equivalent Emissions from Silica
Sand Production in Wisconsin
Natalia Nelson
University of California, Santa Barbara
2015 International Workshop on Environment and Alternative Energy
• Examine relationship between
hydraulic fracturing and climate change
• Calculate numerical quantity of
greenhouse gas emissions released in
life-cycle of hydraulic fracturing
proppant
Purpose
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
What is Hydraulic Fracturing?
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Proppants = Propping Agents
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Thousands of
tons of
proppants
are needed
for each
hydraulic
fracturing
well
Silica Sand
• SiO2
• 99% of all proppants
• 0.4 - 0.8 mm
• ~ 5,000 psi
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
• Currently 40% of
all domestic oil
and natural gas
extraction
• 75% by 2035
• 1.7 million active
wells across the
U.S.
Hydraulic Fracturing Boom
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Silica Sand Boom
0
10,000
20,000
30,000
40,000
50,000
60,000
70,000
80,000
90,000
2008 2010 2012 2014 2016
ThousandsofTons
Year
Nationwide
Production
of Silica
Sand
USGS, 2015
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
• Numerous life-cycle assessments of hydraulic
fracturing have calculated greenhouse gas
emissions
• NONE included emissions from proppant
production
• Other impacts of silica sand production have
been documented but not emissions
Literature Review
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Why is this important?
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
1. What quantity of CO2e emissions is released
from the production and distribution of silica
sand proppant?
2. How do these emissions compare to life-cycle
CO2e emissions of hydraulic fracturing?
3. Should proppant production be included in
future CO2e life cycle analyses of hydraulic
fracturing?
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Research Questions
Wisconsin as a Case Study
• 75% of
domestic
silica sand
production
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Silica Sand Production Process
Mining Processing Transportation
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Production Distribution
Production
Distribution
Total
Calculating CO2e Emissions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
i. Examined 143 facility permits for CO2e
emissions data
I. CO2e Emissions from Production*
*Production was defined as the emissions from the mining, processing, and load
out facilities involved in silica sand production.
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
I. CO2e Emissions from Production
27
53
108
28
143 Facilities' GHG Data from Permits
Unidentified by Air
Permit Search Tool
Identified; No records
Identified; Records;
No CO2e Emissions
Data
Identified; Records;
CO2e Emissions Data
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
I. CO2e Emissions from Production
Out of 143 active mining,
processing, and load out facilities…
Only 28 provided CO2e
data in their permits
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
i. Examined 143 facility permits for CO2e
emissions data
ii. Noted missing data in permits
I. CO2e Emissions from Production
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
i. Examined 143 facility permits for CO2e
emissions data
ii. Noted missing data in permits
iii. Adjusted facility-reported data based
on Northern Industrial Sands document
I. CO2e Emissions from Production
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Northern Industrial Sands Document
• ‘Hourly Data’ – Hours of equipment
usage (time)
• ‘Traffic Data’ – Distance traveled by
vehicles on-site (miles)
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Adjusting Facility-reported Data Based
on Northern Industrial Sands Document
𝒉𝒐𝒖𝒓𝒔 𝒐𝒇 𝒆𝒒𝒖𝒊𝒑𝒎𝒆𝒏𝒕 𝒖𝒔𝒆
𝒚𝒆𝒂𝒓
𝒙
𝒆𝒒𝒖𝒊𝒑𝒎𝒆𝒏𝒕 − 𝒔𝒑𝒆𝒄𝒊𝒇𝒊𝒄 𝒈𝒓𝒂𝒎𝒔 𝑪𝑶 𝟐 𝒓𝒆𝒍𝒆𝒂𝒔𝒆
𝒉𝒐𝒖𝒓
𝒙
𝒕𝒐𝒏
𝒈𝒓𝒂𝒎
=
𝒕𝒐𝒏 𝑪𝑶 𝟐
𝒚𝒆𝒂𝒓
Equation 1: ‘Hourly Data’ CO2 Emissions Calculation
𝒆𝒒𝒖𝒊𝒑𝒎𝒆𝒏𝒕 𝒕𝒓𝒊𝒑𝒔
𝒚𝒆𝒂𝒓
𝒙
𝒇𝒆𝒆𝒕
𝒆𝒒𝒖𝒊𝒑𝒎𝒆𝒏𝒕 𝒕𝒓𝒊𝒑𝒔
𝒙
𝒎𝒊𝒍𝒆
𝒇𝒆𝒆𝒕
𝒙
𝒈𝒂𝒍𝒍𝒐𝒏𝒔 𝒇𝒖𝒆𝒍 𝒖𝒔𝒆𝒅
𝒎𝒊𝒍𝒆
𝒙
𝒕𝒐𝒏 𝑪𝑶 𝟐
𝒈𝒂𝒍𝒍𝒐𝒏𝒔 𝒇𝒖𝒆𝒍 𝒖𝒔𝒆𝒅
=
𝒕𝒐𝒏 𝑪𝑶 𝟐
𝒚𝒆𝒂𝒓
Equation 2: ‘Traffic Data’ CO2 Emissions Calculation
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
i. Examined 143 facility permits for CO2e
emissions data
ii. Noted missing data in permits
iii. Adjusted facility-reported data based on
Northern Industrial Sands Document
iv. Obtained percent increase and extrapolated
statewide
I. CO2e Emissions from Production
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Production
Distribution
Total
Calculating CO2e Emissions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
i. Used low and high estimates of silica sand
outputs from Wisconsin to provide range
- 26 and 40 million tons
ii. Assumed equal distribution to top five
states
- Texas, Louisiana, Colorado, North Dakota, Ohio
II. CO2e Emissions from Distribution*
*Distribution was defined as the emissions from exporting silica sand output to
hydraulic fracturing wells.
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
II. CO2e Emissions from Distribution
Top 5 Destinations for Wisconsin Silica Sand
National Center for Freight
& Infrastructure
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
i. Used high and low estimates of silica sand
output from Wisconsin to provide range
- 26 and 40 million tons
ii. Assumed equal distribution to top five states
- Texas, Louisiana, Colorado, North Dakota, Ohio
iii. Calculated emissions using fuel efficiency rates
of rail and truck transportation
- 30% truck, 70% rail
II. CO2e Emissions from Distribution
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
II. CO2e Emissions from Distribution
𝒕𝒐𝒏𝒔 𝒔𝒂𝒏𝒅 𝒉𝒂𝒖𝒍𝒆𝒅 𝒙 𝒎𝒊𝒍𝒆𝒔 𝒕𝒐 𝒅𝒆𝒔𝒕𝒊𝒏𝒂𝒕𝒊𝒐𝒏 𝒙
𝒈𝒂𝒍𝒍𝒐𝒏 𝒅𝒊𝒆𝒔𝒆𝒍 𝒇𝒖𝒆𝒍
𝒕𝒐𝒏 𝒎𝒊𝒍𝒆𝒔
𝒙
𝒕𝒐𝒏 𝑪𝑶 𝟐
𝒈𝒂𝒍𝒍𝒐𝒏 𝒅𝒊𝒆𝒔𝒆𝒍 𝒇𝒖𝒆𝒍
= 𝒕𝒐𝒏 𝑪𝑶 𝟐
Equation 3: Rail Transportation CO2 Emissions Calculation
𝒎𝒊𝒍𝒆𝒔 𝒕𝒐 𝒅𝒆𝒔𝒕𝒊𝒏𝒂𝒕𝒊𝒐𝒏 𝒙
𝒈𝒂𝒍𝒍𝒐𝒏𝒔 𝒅𝒊𝒆𝒔𝒆𝒍 𝒇𝒖𝒆𝒍
𝒎𝒊𝒍𝒆
𝒙
𝒕𝒐𝒏 𝑪𝑶 𝟐
𝒎𝒊𝒍𝒆
= 𝒕𝒐𝒏 𝑪𝑶 𝟐
Equation 4: Truck Transportation CO2 Emissions Calculation
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
CO2e Emissions from Silica
Sand Production &
Transportation in Wisconsin
(1) Production
Facility Reported
Emissions
NIS Case Study
Calculated
Emissions
Hourly
Data
Percent Increase
in Emissions
Adjusted Facility
Emissions
Total CO2e Emissions from
Silica Sand Production &
Transportation in Wisconsin
Traffic
Data
(2) Distribution
Rail
Combined Rail &
Truck Distribution
Emissions
Truck
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Production
Distribution
Total
Calculating CO2e Emissions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
i. Added Production and Distribution
emissions data together (tonnage)
ii. Converted to emissions per ton silica
sand
iii. Calculated ratio of solely proppant
emissions to total hydraulic fracturing
emissions
III. Total CO2e Emissions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Results
1. How much CO2e emissions are released from
the production and distribution of silica sand
proppant?
- Emissions from Production: ~3.3 million
TPY
- Facility emissions: 5% - 11% higher than
reported
Answering the Research Questions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Production: CO2e Emissions from Wisconsin
Facilities
Lower Estimate (CO2e TPY) 3,247,452
Upper Estimate (CO2e TPY) 3,432,910
Summary of Calculated CO2 Emissions
Data and NIS Provided Data (TPY)
Facility-Reported Data Calculated Estimate
Blasting 149
Sand Dryer 27,311
Total 27,460
Calculated Emissions Data Lower Estimate Upper Estimate
Calculated Hourly Data Totals 345 494
Calculated Traffic Data Totals 1074 2510
Total Additional Emissions 1419 3004
Total Estimated Emissions
(Facility-Reported + Calculated)
28,880 30,465
Percent of Total Emissions Added 5% 11%
1. How much CO2e emissions are released from
the production and distribution of silica sand
proppant?
- Emissions from Production: ~3.3 million
TPY
- Facility emissions: 5% - 11% higher than
reported
- Adjusted Facility Average: 34,000 tons CO2e
emissions per year
Answering the Research Questions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Adjusted CO2e Facility Emissions (TPY)
Facility
No.
FID Reported CO2e
Emissions
Adjusted Low Estimate
(5% increase)
Adjusted High Estimate
(11% increase)
1 662029940 28,597 30,027 31,742
2 627007260 62,102 65,207 68,933
3 662030380 1,585 1,664 1,759
4 772151270 9,800 10,290 10,878
5 603107010 44,000 46,200 48,840
6 610078590 30,000 31,500 33,300
7 609128960 38,894 40,839 43,172
8 772145770 18,922 19,868 21,003
9 662031150 11,019 11,570 12,231
10 603106680 70,996 74,545 78,806
11 662067560 60,733 63,770 67,414
12 662068110 1,379 1,448 1,531
13 662069540 715 751 794
14 610079140 636 668 706
15 662031040 21,034 22,086 23,348
16 603111190 27,473 28,847 30,495
17 612018550 55 58 61
18 662028620 18,566 19,494 20,608
19 662070090 28,672 30,106 31,826
20 729038640 24,449 25,672 27,138
21 603111410 28,620 30,051 31,768
22 627023210 57,158 60,016 63,445
23 855010310 46, 121 48,427 51,194
24 603110860 57,967 60,865 64,343
25 627021670 12,083 12,687 13,412
26 642078800 45,862 48,155 50,907
27 648017920 121,600 127,680 134,976
28 642028420 21,880 22,974 24,287
Facility Average 33,410 35,318
1. How much CO2e emissions are released from the
production and distribution of silica sand
proppant?
- Emissions from Production: ~3.3 million TPY
- Facility emissions: 5% - 11% higher than reported
- Adjusted Facility Average: 34,000 tons CO2e
emissions per year
- Emissions from Distribution: ~1.2 million TPY
Answering the Research Questions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Distribution: CO2e Emissions from Rail and
Truck Transportation
Lower Estimate (CO2e TPY) 936,356
Upper Estimate (CO2e TPY) 1,440,349
1. How much CO2e emissions are released from the
production and distribution of silica sand
proppant?
- Emissions from Production: ~3.3 million TPY
- Facility emissions: 5% - 11% higher than reported
- Adjusted Facility Average: 34,000 tons CO2e
emissions per year
- Emissions from Distribution: ~1.2 million TPY
- Total: ~4.5 million TPY
Answering the Research Questions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Total: Silica Sand Proppant Production and
Distribution CO2e Emissions in Wisconsin
Lower Estimate
(TPY)
Upper Estimate
(TPY)
Production 3,247,452 3,432,910
Distribution 936,356 1,440,349
Total 4,183,808 4,873,259
Equivalent to annual greenhouse gas emissions from
860,000 passenger vehicles
- 0.15 ton CO2e per ton silica sand
produced
- 5-34% increase in emissions if LCAs of
hydraulic fracturing included proppant
production
Answering the Research Questions
2. How do these emissions compare to life cycle
CO2e emissions of hydraulic fracturing?
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Summary of Percent Increase in Overall
Hydraulic Fracturing Emissions due to Silica
Sand Production
Authors Scope Finding
(t CO2e
per well)
Percent Increase in Emissions of
Silica Sand Production
Lower Estimate Upper Estimate
O’Sullivan &
Paltsev (2011)
Least extensive; only
emissions during
natural gas
production; CH4
emissions only
1,378 19% 34%
Griffith et al.
(2011)
Extensive; well
development to
completion; specific
to Marcellus Shale
5,500 15% 27%
MacKay &
Stone (2013)
Most extensive; well
development to
completion and
additional elements
4,887 5% 10%
Answering the Research Questions
3. Should proppant production be included in
future life cycle analyses of CO2e
calculations of hydraulic fracturing?
Yes!
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
• Tremendous need for facility greenhouse gas
data
• Proppant production emissions absent from
hydraulic fracturing GHG research
• A 5-34% increase in life cycle assessment
calculations of hydraulic fracturing is extremely
significant for policy-makers, scientists, and the
public
Conclusions
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
• Reduce distance between mine site and processing
site
• Upgrade equipment efficiency
• Switch transportation method from truck to rail (3x
more efficient)
• Recover and re-use proppants
• Regulate facility emissions with a long-term system of
greenhouse gas monitoring
Recommendations for
Emissions Reduction
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
• Replace assumptions with hard data
• Reach beyond the scope of Wisconsin
• Examine the feasibility and efficiency
of proppant recovery and recycling
after use.
Future Research
Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
Acknowledgements
Silica Sand Granules: BuyProppant.com, 2015
Wisconsin Outline: WisconsinWatch.org, 2013
Silica Sand Machinery: Sircon.com, 2014
Temperature and Carbon Dioxide Graph: zFacts.com, 2010
Wildfires in California: The Guardian, 2013
Fulsom Dam: Justin Sullivan, 2014
Hurricane Patricia: Scott Kelly, 2015
Hydraulic Fracturing Graphic: Getty, 2013
Sand Acts as a Proppant in Hydraulic Fracturing: U.S. Global Investors, 2014
Silica Sand Pile: Broadmoor, 2015
Silica Sand Processing: Foundry Silica, 2015
Fracking Sand: Minnesota Environmental Quality Board, 2013
Frac Sand Semi Truck: Twincities.com, 2014
Aerial View of Kosse Mine: Superior Silica Sands, 2015
Cambrian and Ordovician Sandstone Formations: Reed, 2005
Aerial view of Clinton Mine: Superior Silica Sands, 2015.
Aerial View of New Auburn Plant: Superior Silica Sands, 2015.
Wisconsin Silica Sand Facilities: WisconsinWatch.org, 2014
Top U.S. Destinations for Silica Sand: National Center for Freight and Infrastructure, 2013
Image Sources
Thank you!
Questions?

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Final Climate Change and Hydraulic Fracturing Proppants

  • 1. Climate Change and Hydraulic Fracturing Proppants: Calculating the Carbon Dioxide Equivalent Emissions from Silica Sand Production in Wisconsin Natalia Nelson University of California, Santa Barbara 2015 International Workshop on Environment and Alternative Energy
  • 2. • Examine relationship between hydraulic fracturing and climate change • Calculate numerical quantity of greenhouse gas emissions released in life-cycle of hydraulic fracturing proppant Purpose Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 3. What is Hydraulic Fracturing? Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 4. Proppants = Propping Agents Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions Thousands of tons of proppants are needed for each hydraulic fracturing well
  • 5. Silica Sand • SiO2 • 99% of all proppants • 0.4 - 0.8 mm • ~ 5,000 psi Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 6. • Currently 40% of all domestic oil and natural gas extraction • 75% by 2035 • 1.7 million active wells across the U.S. Hydraulic Fracturing Boom Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 7. Silica Sand Boom 0 10,000 20,000 30,000 40,000 50,000 60,000 70,000 80,000 90,000 2008 2010 2012 2014 2016 ThousandsofTons Year Nationwide Production of Silica Sand USGS, 2015 Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 8. • Numerous life-cycle assessments of hydraulic fracturing have calculated greenhouse gas emissions • NONE included emissions from proppant production • Other impacts of silica sand production have been documented but not emissions Literature Review Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 9. Why is this important? Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 10. 1. What quantity of CO2e emissions is released from the production and distribution of silica sand proppant? 2. How do these emissions compare to life-cycle CO2e emissions of hydraulic fracturing? 3. Should proppant production be included in future CO2e life cycle analyses of hydraulic fracturing? Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions Research Questions
  • 11. Wisconsin as a Case Study • 75% of domestic silica sand production Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 12. Silica Sand Production Process Mining Processing Transportation Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions Production Distribution
  • 13. Production Distribution Total Calculating CO2e Emissions Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 14. i. Examined 143 facility permits for CO2e emissions data I. CO2e Emissions from Production* *Production was defined as the emissions from the mining, processing, and load out facilities involved in silica sand production. Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 15. I. CO2e Emissions from Production 27 53 108 28 143 Facilities' GHG Data from Permits Unidentified by Air Permit Search Tool Identified; No records Identified; Records; No CO2e Emissions Data Identified; Records; CO2e Emissions Data Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 16. I. CO2e Emissions from Production Out of 143 active mining, processing, and load out facilities… Only 28 provided CO2e data in their permits Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 17. i. Examined 143 facility permits for CO2e emissions data ii. Noted missing data in permits I. CO2e Emissions from Production Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 18. Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 19. i. Examined 143 facility permits for CO2e emissions data ii. Noted missing data in permits iii. Adjusted facility-reported data based on Northern Industrial Sands document I. CO2e Emissions from Production Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 20. Northern Industrial Sands Document • ‘Hourly Data’ – Hours of equipment usage (time) • ‘Traffic Data’ – Distance traveled by vehicles on-site (miles) Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 21. Adjusting Facility-reported Data Based on Northern Industrial Sands Document 𝒉𝒐𝒖𝒓𝒔 𝒐𝒇 𝒆𝒒𝒖𝒊𝒑𝒎𝒆𝒏𝒕 𝒖𝒔𝒆 𝒚𝒆𝒂𝒓 𝒙 𝒆𝒒𝒖𝒊𝒑𝒎𝒆𝒏𝒕 − 𝒔𝒑𝒆𝒄𝒊𝒇𝒊𝒄 𝒈𝒓𝒂𝒎𝒔 𝑪𝑶 𝟐 𝒓𝒆𝒍𝒆𝒂𝒔𝒆 𝒉𝒐𝒖𝒓 𝒙 𝒕𝒐𝒏 𝒈𝒓𝒂𝒎 = 𝒕𝒐𝒏 𝑪𝑶 𝟐 𝒚𝒆𝒂𝒓 Equation 1: ‘Hourly Data’ CO2 Emissions Calculation 𝒆𝒒𝒖𝒊𝒑𝒎𝒆𝒏𝒕 𝒕𝒓𝒊𝒑𝒔 𝒚𝒆𝒂𝒓 𝒙 𝒇𝒆𝒆𝒕 𝒆𝒒𝒖𝒊𝒑𝒎𝒆𝒏𝒕 𝒕𝒓𝒊𝒑𝒔 𝒙 𝒎𝒊𝒍𝒆 𝒇𝒆𝒆𝒕 𝒙 𝒈𝒂𝒍𝒍𝒐𝒏𝒔 𝒇𝒖𝒆𝒍 𝒖𝒔𝒆𝒅 𝒎𝒊𝒍𝒆 𝒙 𝒕𝒐𝒏 𝑪𝑶 𝟐 𝒈𝒂𝒍𝒍𝒐𝒏𝒔 𝒇𝒖𝒆𝒍 𝒖𝒔𝒆𝒅 = 𝒕𝒐𝒏 𝑪𝑶 𝟐 𝒚𝒆𝒂𝒓 Equation 2: ‘Traffic Data’ CO2 Emissions Calculation Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 22. i. Examined 143 facility permits for CO2e emissions data ii. Noted missing data in permits iii. Adjusted facility-reported data based on Northern Industrial Sands Document iv. Obtained percent increase and extrapolated statewide I. CO2e Emissions from Production Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 23. Production Distribution Total Calculating CO2e Emissions Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 24. i. Used low and high estimates of silica sand outputs from Wisconsin to provide range - 26 and 40 million tons ii. Assumed equal distribution to top five states - Texas, Louisiana, Colorado, North Dakota, Ohio II. CO2e Emissions from Distribution* *Distribution was defined as the emissions from exporting silica sand output to hydraulic fracturing wells. Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 25. II. CO2e Emissions from Distribution Top 5 Destinations for Wisconsin Silica Sand National Center for Freight & Infrastructure Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 26. i. Used high and low estimates of silica sand output from Wisconsin to provide range - 26 and 40 million tons ii. Assumed equal distribution to top five states - Texas, Louisiana, Colorado, North Dakota, Ohio iii. Calculated emissions using fuel efficiency rates of rail and truck transportation - 30% truck, 70% rail II. CO2e Emissions from Distribution Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 27. II. CO2e Emissions from Distribution 𝒕𝒐𝒏𝒔 𝒔𝒂𝒏𝒅 𝒉𝒂𝒖𝒍𝒆𝒅 𝒙 𝒎𝒊𝒍𝒆𝒔 𝒕𝒐 𝒅𝒆𝒔𝒕𝒊𝒏𝒂𝒕𝒊𝒐𝒏 𝒙 𝒈𝒂𝒍𝒍𝒐𝒏 𝒅𝒊𝒆𝒔𝒆𝒍 𝒇𝒖𝒆𝒍 𝒕𝒐𝒏 𝒎𝒊𝒍𝒆𝒔 𝒙 𝒕𝒐𝒏 𝑪𝑶 𝟐 𝒈𝒂𝒍𝒍𝒐𝒏 𝒅𝒊𝒆𝒔𝒆𝒍 𝒇𝒖𝒆𝒍 = 𝒕𝒐𝒏 𝑪𝑶 𝟐 Equation 3: Rail Transportation CO2 Emissions Calculation 𝒎𝒊𝒍𝒆𝒔 𝒕𝒐 𝒅𝒆𝒔𝒕𝒊𝒏𝒂𝒕𝒊𝒐𝒏 𝒙 𝒈𝒂𝒍𝒍𝒐𝒏𝒔 𝒅𝒊𝒆𝒔𝒆𝒍 𝒇𝒖𝒆𝒍 𝒎𝒊𝒍𝒆 𝒙 𝒕𝒐𝒏 𝑪𝑶 𝟐 𝒎𝒊𝒍𝒆 = 𝒕𝒐𝒏 𝑪𝑶 𝟐 Equation 4: Truck Transportation CO2 Emissions Calculation Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 28. CO2e Emissions from Silica Sand Production & Transportation in Wisconsin (1) Production Facility Reported Emissions NIS Case Study Calculated Emissions Hourly Data Percent Increase in Emissions Adjusted Facility Emissions Total CO2e Emissions from Silica Sand Production & Transportation in Wisconsin Traffic Data (2) Distribution Rail Combined Rail & Truck Distribution Emissions Truck Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 29. Production Distribution Total Calculating CO2e Emissions Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 30. i. Added Production and Distribution emissions data together (tonnage) ii. Converted to emissions per ton silica sand iii. Calculated ratio of solely proppant emissions to total hydraulic fracturing emissions III. Total CO2e Emissions Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 31. Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 33. 1. How much CO2e emissions are released from the production and distribution of silica sand proppant? - Emissions from Production: ~3.3 million TPY - Facility emissions: 5% - 11% higher than reported Answering the Research Questions Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions Production: CO2e Emissions from Wisconsin Facilities Lower Estimate (CO2e TPY) 3,247,452 Upper Estimate (CO2e TPY) 3,432,910
  • 34. Summary of Calculated CO2 Emissions Data and NIS Provided Data (TPY) Facility-Reported Data Calculated Estimate Blasting 149 Sand Dryer 27,311 Total 27,460 Calculated Emissions Data Lower Estimate Upper Estimate Calculated Hourly Data Totals 345 494 Calculated Traffic Data Totals 1074 2510 Total Additional Emissions 1419 3004 Total Estimated Emissions (Facility-Reported + Calculated) 28,880 30,465 Percent of Total Emissions Added 5% 11%
  • 35. 1. How much CO2e emissions are released from the production and distribution of silica sand proppant? - Emissions from Production: ~3.3 million TPY - Facility emissions: 5% - 11% higher than reported - Adjusted Facility Average: 34,000 tons CO2e emissions per year Answering the Research Questions Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 36. Adjusted CO2e Facility Emissions (TPY) Facility No. FID Reported CO2e Emissions Adjusted Low Estimate (5% increase) Adjusted High Estimate (11% increase) 1 662029940 28,597 30,027 31,742 2 627007260 62,102 65,207 68,933 3 662030380 1,585 1,664 1,759 4 772151270 9,800 10,290 10,878 5 603107010 44,000 46,200 48,840 6 610078590 30,000 31,500 33,300 7 609128960 38,894 40,839 43,172 8 772145770 18,922 19,868 21,003 9 662031150 11,019 11,570 12,231 10 603106680 70,996 74,545 78,806 11 662067560 60,733 63,770 67,414 12 662068110 1,379 1,448 1,531 13 662069540 715 751 794 14 610079140 636 668 706 15 662031040 21,034 22,086 23,348 16 603111190 27,473 28,847 30,495 17 612018550 55 58 61 18 662028620 18,566 19,494 20,608 19 662070090 28,672 30,106 31,826 20 729038640 24,449 25,672 27,138 21 603111410 28,620 30,051 31,768 22 627023210 57,158 60,016 63,445 23 855010310 46, 121 48,427 51,194 24 603110860 57,967 60,865 64,343 25 627021670 12,083 12,687 13,412 26 642078800 45,862 48,155 50,907 27 648017920 121,600 127,680 134,976 28 642028420 21,880 22,974 24,287 Facility Average 33,410 35,318
  • 37. 1. How much CO2e emissions are released from the production and distribution of silica sand proppant? - Emissions from Production: ~3.3 million TPY - Facility emissions: 5% - 11% higher than reported - Adjusted Facility Average: 34,000 tons CO2e emissions per year - Emissions from Distribution: ~1.2 million TPY Answering the Research Questions Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 38. Distribution: CO2e Emissions from Rail and Truck Transportation Lower Estimate (CO2e TPY) 936,356 Upper Estimate (CO2e TPY) 1,440,349
  • 39. 1. How much CO2e emissions are released from the production and distribution of silica sand proppant? - Emissions from Production: ~3.3 million TPY - Facility emissions: 5% - 11% higher than reported - Adjusted Facility Average: 34,000 tons CO2e emissions per year - Emissions from Distribution: ~1.2 million TPY - Total: ~4.5 million TPY Answering the Research Questions Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 40. Total: Silica Sand Proppant Production and Distribution CO2e Emissions in Wisconsin Lower Estimate (TPY) Upper Estimate (TPY) Production 3,247,452 3,432,910 Distribution 936,356 1,440,349 Total 4,183,808 4,873,259 Equivalent to annual greenhouse gas emissions from 860,000 passenger vehicles
  • 41. - 0.15 ton CO2e per ton silica sand produced - 5-34% increase in emissions if LCAs of hydraulic fracturing included proppant production Answering the Research Questions 2. How do these emissions compare to life cycle CO2e emissions of hydraulic fracturing? Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 42. Summary of Percent Increase in Overall Hydraulic Fracturing Emissions due to Silica Sand Production Authors Scope Finding (t CO2e per well) Percent Increase in Emissions of Silica Sand Production Lower Estimate Upper Estimate O’Sullivan & Paltsev (2011) Least extensive; only emissions during natural gas production; CH4 emissions only 1,378 19% 34% Griffith et al. (2011) Extensive; well development to completion; specific to Marcellus Shale 5,500 15% 27% MacKay & Stone (2013) Most extensive; well development to completion and additional elements 4,887 5% 10%
  • 43. Answering the Research Questions 3. Should proppant production be included in future life cycle analyses of CO2e calculations of hydraulic fracturing? Yes! Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 44. • Tremendous need for facility greenhouse gas data • Proppant production emissions absent from hydraulic fracturing GHG research • A 5-34% increase in life cycle assessment calculations of hydraulic fracturing is extremely significant for policy-makers, scientists, and the public Conclusions Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 45. • Reduce distance between mine site and processing site • Upgrade equipment efficiency • Switch transportation method from truck to rail (3x more efficient) • Recover and re-use proppants • Regulate facility emissions with a long-term system of greenhouse gas monitoring Recommendations for Emissions Reduction Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 46. • Replace assumptions with hard data • Reach beyond the scope of Wisconsin • Examine the feasibility and efficiency of proppant recovery and recycling after use. Future Research Purpose  Background  Rationale  Research Questions  Methods  Results  Conclusions
  • 48. Silica Sand Granules: BuyProppant.com, 2015 Wisconsin Outline: WisconsinWatch.org, 2013 Silica Sand Machinery: Sircon.com, 2014 Temperature and Carbon Dioxide Graph: zFacts.com, 2010 Wildfires in California: The Guardian, 2013 Fulsom Dam: Justin Sullivan, 2014 Hurricane Patricia: Scott Kelly, 2015 Hydraulic Fracturing Graphic: Getty, 2013 Sand Acts as a Proppant in Hydraulic Fracturing: U.S. Global Investors, 2014 Silica Sand Pile: Broadmoor, 2015 Silica Sand Processing: Foundry Silica, 2015 Fracking Sand: Minnesota Environmental Quality Board, 2013 Frac Sand Semi Truck: Twincities.com, 2014 Aerial View of Kosse Mine: Superior Silica Sands, 2015 Cambrian and Ordovician Sandstone Formations: Reed, 2005 Aerial view of Clinton Mine: Superior Silica Sands, 2015. Aerial View of New Auburn Plant: Superior Silica Sands, 2015. Wisconsin Silica Sand Facilities: WisconsinWatch.org, 2014 Top U.S. Destinations for Silica Sand: National Center for Freight and Infrastructure, 2013 Image Sources

Notes de l'éditeur

  1. Only 20% of all the facilities provided any co2e data
  2. I had to make a huge assumption that the sand was equally traveling to the top five states This is a large assumption, but it was outside the scope of my research to exactly determine wehre all the silica sand was going.
  3. Under assumption that well uses 2,500 tons per proppant (low estimate, as shale wells can use up to 10,000)
  4. - Wisconsin’s annual emissions in 2015 were calculated at 110 million per year, so approximately 4.5 million is a significant portion of emissions. (4%)
  5. This lack of data likely accounts for the lack of research/studies on proppant emissions (Is it because the information is proprietary and unavailable to public or because it does not exist?) No incentive / regulation to reduce GHGs if they are unreported / undocumented
  6. This research was an exploration of the topic, and from a lack of data it was difficult to calculate specifics. As soon as more data is gathered, further research can be carried out. This is just one of many studies that should be done to fully qualify and ultimately reduce emissions from proppant production.