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Lindsay A. House
Daniel M. Downey
James Madison University
Department of Chemistry and Biochemistry
A Tale of Two Appalachian Highland
Streams: Acid Mitigation Planning and
Results
Little Tumbling Creek (LTC) and
North Fork Stony Creek (NFSC)
Blue – LTC
Red - NFSC
Acid Rain
 More acidic than natural rain (pH < 5). HNO3 and H2SO4.
 SOx and NOx emissions from coal fired power plants and
vehicles form anthropogenic atmospheric acid.
 Regional rainfall shows elevated acid levels due to
anthropogenic atmospheric acid.
Effect of Acid Rain on Stream Chemistry
 Acid-sensitive flora and fauna are inhibited in acidic water
 Weathering of geology – dissolved ions constitute stream chemistry
 (Ca2+) + (Mg2+) + (Na+) + (K+) = (Cl-) + (NO3
-) + (SO4
2-) + (HCO3
-)
 Bicarbonate is the only ionic ingredient that reacts with acid. This
contributes to the acid neutralizing capacity (ANC) of the stream
 Streams that discharge from low carbonate geology show large pH
decreases and a loss of ANC from acid injections during precipitation
events
Two Appalachian Highland
Streams
Little Tumbling Creek North Fork Stony Creek
 Located in Smyth and Tazewell
Counties, VA
 Clinch Mountain Wildlife
Management Area (VDGIF)
 Atmospheric acid deposition
caused upper four miles of
creek to lose its brook trout
population
 Devoid of fish for over 20 years
 Limed Jan. 2012 – 60 tons
 Located in Giles Co., VA at Glen
Alton
 Jefferson National Forest
(USFS)
 Depressed fish population due
to acidic stream conditions
 Candidate for liming
Stream Comparison
LTC NFSC
Watershed Area (ha) 2308 2243
Total Stream Reach (km) 11.9 6.3
Average Precipitation (m/year) 1.26 1.26
Uppermost elevation (m) 1125 989
Lowermost elevation (m) 690 786
Discharge (m3/year) 1.7 x 107 1.7 x 107
H & NH4 influx (keq/year) 403 392
Limestone Treatment Requirement
(tonnes/year)
20 20
Treatment Stream Reach (km) 9.9 5.6
Little Tumbling Creek Geology
 Omb – Martinsburg Shale
 D – Devonian rocks; S – Silurian
Rocks
 Oml – Limestone formations
http://ngmdb.usgs.gov/ngmdb/ngmdb_home.html
Liming of Little Tumbling Creek
 Limestone (93% CaCO3,
12 x 120 mesh) delivered on
January 31, 2002 by Global
Stone Corporation.
 Limed in Jan. 2012 because
of a new road made possible
by American Electric Power
(AEP). Total of 60 tons.
 4000 Northern strain triploid
brook trout released into
stream in May 2012 and
2013. Triploids are
placeholders for future
Southern strain brook trout.
Sample Collection
 Synoptic Sampling
 Samples are collected at multiple sites to provide
detailed water chemistry data from headwaters to
downstream
 Quarterly Sampling
 Samples are collected seasonally at selective sites
from headwaters to downstream
Sample Analysis
 All samples analyzed for pH, base metal cations
(Ca2+, Mg2+, Na+, K+), major acid anions (Cl-,
SO4
2-, NO3
-), acid neutralizing capacity (ANC),
and aluminum (AlT) concentrations.
 Ion chromatography (Dionex ICS 3000) used for
base metal cations and major acid anions.
 Air equilibrated pH and alkalinity values found at
20 °C.
 Elemental concentrations of aluminum were
measured using inductively coupled plasma-mass
spectrometry (Agilent ICP-MS 7500).
LTC Sampling Sites
LTC Synoptic Water Chemistry
Site Elevatio
n (ft)
pH ANC Ca Al Ca/H
μeq/L ppb
1 2248 5.96 14.6 77.1 33 70.32
1A 2331 5.59 4.9 64.2 42 24.98
1B 2435 5.59 5.7 65.9 48 25.64
2 2654 5.65 8.9 67.0 42 29.93
3 2723 5.54 4.9 67.6 51 23.44
3A 2756 5.30 1.6 64.9 64 12.95
3B 2797 5.58 6.1 69.4 54 26.39
4 3016 5.81 8.5 77.9 54 50.30
5 3333 5.99 24.8 115.1 81 112.48
6 3319 5.10 -2.0 62.7 124 7.89
7 3335 4.92 -7.7 52.0 136 4.33
8 3423 4.67 -21.9 24.0 213 1.12
July 2013 Sampling
2012-2013 Quarterly Data
Consumption Rate of Limestone
LTC Future Work
 Continue monitoring water
chemistry in LTC
 Introduce 40 tons of additional
Aglime limestone to increase
pH and ANC
 Use the results of LTC liming to
guide proposal for liming NFSC
North Fork Stony Creek History
 USFS has 100% ownership of NFSC.
 Headwaters acquired in 1920s
 Glen Alton – farm/vacation retreat from 1930s until 1980s;
located on lower reaches of NFSC. Purchased by USFS in 1999.
 1993 – Large woody debris study. Logs added to stream as
experimental restoration technique (Dolloff).
North Fork Stony Creek Geology
 Stu – Tuscarora
Formation
 Srh – Rose Hill Formation
 Stk – Tonoloway
Limestone and Keefer
Sandstone
 Dhr – Huntersville
Formation
 Dm – Millboro Formation
http://ngmdb.usgs.gov/ngmdb/ngmdb_home.html
NFSC Sampling Sites
Trends in ANC 1987 - Present
NFSC Water Chemistry 1987-
2013
Fall Winter Spring Summer
Average pH 5.85 ± 0.29 5.38 ± 0.29 5.36 ± 0.18 5.69 ± 0.26
Average ANC
(μeq/L)
17.4 ± 9.7 4.7 ± 6.7 3.8 ± 4.0 15.4 ± 7.1
Average pH and ANC at VT 28: 1987-2013
NFSC Synoptic Water Chemistry
Site Elevation
(ft)
pH ANC Ca Al Ca/H
μeq/L ppb
July 2013
3 2611 5.31 -1.6 1.5 12 0.31
10 2945 5.07 -6.9 1.6 19 0.19
October
2013
3 2611 5.96 14.2 35 31 31.92
4 2631 6.05 19.9 35.1 31 39.38
5 2855 5.77 15.0 32.9 40 19.37
6 2872 5.87 17.5 32.2 42 23.87
7 2887 5.67 13.8 32.8 54 15.34
8 2936 5.76 13.0 32.9 56 18.93
9 2940 5.61 8.5 31 60 12.63
10 2945 5.59 8.5 29.5 62 11.48
Dixon 1 2874 5.34 -5.3 20.2 57 4.42
Dixon 2 2889 5.16 -4.5 23.3 75 3.37
NFSC Future Work
 Continue monitoring water
chemistry
 Design low-cost plan for
limestone treatment
 The addition of 100 tons of
limestone from a nearby quarry
 Reestablish brook trout
populations and other aquatic life
Acknowledgements
 Bill Kittrell (VDGIF)
 George Palmer (VDGIF)
 Dawn Kirk (USFS)
 Steve DeFranco
(USFS)
 Jacob Roodman
 Sydney Fisher
 National Science
Foundation - CHE-
1062629
 U.S. Forest Service
 Virginia Department of
Game and Inland
Fisheries

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AFS_Presentation_Housela_updated

  • 1. Lindsay A. House Daniel M. Downey James Madison University Department of Chemistry and Biochemistry A Tale of Two Appalachian Highland Streams: Acid Mitigation Planning and Results
  • 2. Little Tumbling Creek (LTC) and North Fork Stony Creek (NFSC) Blue – LTC Red - NFSC
  • 3. Acid Rain  More acidic than natural rain (pH < 5). HNO3 and H2SO4.  SOx and NOx emissions from coal fired power plants and vehicles form anthropogenic atmospheric acid.  Regional rainfall shows elevated acid levels due to anthropogenic atmospheric acid.
  • 4. Effect of Acid Rain on Stream Chemistry  Acid-sensitive flora and fauna are inhibited in acidic water  Weathering of geology – dissolved ions constitute stream chemistry  (Ca2+) + (Mg2+) + (Na+) + (K+) = (Cl-) + (NO3 -) + (SO4 2-) + (HCO3 -)  Bicarbonate is the only ionic ingredient that reacts with acid. This contributes to the acid neutralizing capacity (ANC) of the stream  Streams that discharge from low carbonate geology show large pH decreases and a loss of ANC from acid injections during precipitation events
  • 5. Two Appalachian Highland Streams Little Tumbling Creek North Fork Stony Creek  Located in Smyth and Tazewell Counties, VA  Clinch Mountain Wildlife Management Area (VDGIF)  Atmospheric acid deposition caused upper four miles of creek to lose its brook trout population  Devoid of fish for over 20 years  Limed Jan. 2012 – 60 tons  Located in Giles Co., VA at Glen Alton  Jefferson National Forest (USFS)  Depressed fish population due to acidic stream conditions  Candidate for liming
  • 6. Stream Comparison LTC NFSC Watershed Area (ha) 2308 2243 Total Stream Reach (km) 11.9 6.3 Average Precipitation (m/year) 1.26 1.26 Uppermost elevation (m) 1125 989 Lowermost elevation (m) 690 786 Discharge (m3/year) 1.7 x 107 1.7 x 107 H & NH4 influx (keq/year) 403 392 Limestone Treatment Requirement (tonnes/year) 20 20 Treatment Stream Reach (km) 9.9 5.6
  • 7. Little Tumbling Creek Geology  Omb – Martinsburg Shale  D – Devonian rocks; S – Silurian Rocks  Oml – Limestone formations http://ngmdb.usgs.gov/ngmdb/ngmdb_home.html
  • 8. Liming of Little Tumbling Creek  Limestone (93% CaCO3, 12 x 120 mesh) delivered on January 31, 2002 by Global Stone Corporation.  Limed in Jan. 2012 because of a new road made possible by American Electric Power (AEP). Total of 60 tons.  4000 Northern strain triploid brook trout released into stream in May 2012 and 2013. Triploids are placeholders for future Southern strain brook trout.
  • 9. Sample Collection  Synoptic Sampling  Samples are collected at multiple sites to provide detailed water chemistry data from headwaters to downstream  Quarterly Sampling  Samples are collected seasonally at selective sites from headwaters to downstream
  • 10. Sample Analysis  All samples analyzed for pH, base metal cations (Ca2+, Mg2+, Na+, K+), major acid anions (Cl-, SO4 2-, NO3 -), acid neutralizing capacity (ANC), and aluminum (AlT) concentrations.  Ion chromatography (Dionex ICS 3000) used for base metal cations and major acid anions.  Air equilibrated pH and alkalinity values found at 20 °C.  Elemental concentrations of aluminum were measured using inductively coupled plasma-mass spectrometry (Agilent ICP-MS 7500).
  • 12. LTC Synoptic Water Chemistry Site Elevatio n (ft) pH ANC Ca Al Ca/H μeq/L ppb 1 2248 5.96 14.6 77.1 33 70.32 1A 2331 5.59 4.9 64.2 42 24.98 1B 2435 5.59 5.7 65.9 48 25.64 2 2654 5.65 8.9 67.0 42 29.93 3 2723 5.54 4.9 67.6 51 23.44 3A 2756 5.30 1.6 64.9 64 12.95 3B 2797 5.58 6.1 69.4 54 26.39 4 3016 5.81 8.5 77.9 54 50.30 5 3333 5.99 24.8 115.1 81 112.48 6 3319 5.10 -2.0 62.7 124 7.89 7 3335 4.92 -7.7 52.0 136 4.33 8 3423 4.67 -21.9 24.0 213 1.12 July 2013 Sampling
  • 14. Consumption Rate of Limestone
  • 15. LTC Future Work  Continue monitoring water chemistry in LTC  Introduce 40 tons of additional Aglime limestone to increase pH and ANC  Use the results of LTC liming to guide proposal for liming NFSC
  • 16. North Fork Stony Creek History  USFS has 100% ownership of NFSC.  Headwaters acquired in 1920s  Glen Alton – farm/vacation retreat from 1930s until 1980s; located on lower reaches of NFSC. Purchased by USFS in 1999.  1993 – Large woody debris study. Logs added to stream as experimental restoration technique (Dolloff).
  • 17. North Fork Stony Creek Geology  Stu – Tuscarora Formation  Srh – Rose Hill Formation  Stk – Tonoloway Limestone and Keefer Sandstone  Dhr – Huntersville Formation  Dm – Millboro Formation http://ngmdb.usgs.gov/ngmdb/ngmdb_home.html
  • 19. Trends in ANC 1987 - Present
  • 20. NFSC Water Chemistry 1987- 2013 Fall Winter Spring Summer Average pH 5.85 ± 0.29 5.38 ± 0.29 5.36 ± 0.18 5.69 ± 0.26 Average ANC (μeq/L) 17.4 ± 9.7 4.7 ± 6.7 3.8 ± 4.0 15.4 ± 7.1 Average pH and ANC at VT 28: 1987-2013
  • 21. NFSC Synoptic Water Chemistry Site Elevation (ft) pH ANC Ca Al Ca/H μeq/L ppb July 2013 3 2611 5.31 -1.6 1.5 12 0.31 10 2945 5.07 -6.9 1.6 19 0.19 October 2013 3 2611 5.96 14.2 35 31 31.92 4 2631 6.05 19.9 35.1 31 39.38 5 2855 5.77 15.0 32.9 40 19.37 6 2872 5.87 17.5 32.2 42 23.87 7 2887 5.67 13.8 32.8 54 15.34 8 2936 5.76 13.0 32.9 56 18.93 9 2940 5.61 8.5 31 60 12.63 10 2945 5.59 8.5 29.5 62 11.48 Dixon 1 2874 5.34 -5.3 20.2 57 4.42 Dixon 2 2889 5.16 -4.5 23.3 75 3.37
  • 22. NFSC Future Work  Continue monitoring water chemistry  Design low-cost plan for limestone treatment  The addition of 100 tons of limestone from a nearby quarry  Reestablish brook trout populations and other aquatic life
  • 23. Acknowledgements  Bill Kittrell (VDGIF)  George Palmer (VDGIF)  Dawn Kirk (USFS)  Steve DeFranco (USFS)  Jacob Roodman  Sydney Fisher  National Science Foundation - CHE- 1062629  U.S. Forest Service  Virginia Department of Game and Inland Fisheries

Editor's Notes

  1. Stk – some limestone, but not enough to affect water chemistry. Everything else = sandstone or shale