1960 1995 Ground Water Age and Chemistry Data along Flow Paths: Implications for Trends d Transformations of Nutrients and Pesticide Jim Tesoriero, Karen Burow, Betsy Frick, David Saad, Larry Puckett U.S. Geological Survey
Jan 04, 2016
19601995
Ground Water Age and Chemistry Data along Flow Paths: Implications for Trends
and Transformations of Nutrients and PesticidesJim Tesoriero, Karen Burow, Betsy Frick, David Saad, Larry Puckett
U.S. Geological Survey
Increased influx of nutrients and pesticides Five-fold increase in nitrogen fertilizer applied since 1960
Commonly used herbicides introduced
What are the implications for ground water quality?
0
2
4
6
8
10
12
1940 1950 1960 1970 1980 1990 2000
Mil
lion
s of
Met
ric
Ton
s P
er Y
ear N Fertilizer
Atrazine Alachlor
Pesticides Introduced:
Metolachlor
NO3-→N2
Study Objectives: 1) Determine and explain trends in concentrations.
2) Determine where transformations occur.
19901990
1985 1980
19801975
1970
1950
2000
1960
1970
1. Determine recharge dates of ground water along flow pathsDesign:
2. Characterize water chemistry and natural attenuation 3. Compare constituent concentrations to loading history
Nutrient and Pesticide Application
Reactions
Redox Zone DO
NO3- or N2
IronAerobic Respiration:
O2 H2OOxic High NO3
- Low
Denitrification:
NO3- N2
Nitrate-reducing
Low NO3
- N2Low
Ferric Iron Reduction:
Fe3+ Fe2+
Iron-reducing
Low N2 High
Natural Attenuation: Redox Reactions Important in Determining Fate of Constituents
Water Chemistry
Western Lake Michigan Drainages
Wisconsin
Albemarle-Pamlico Basin
North Carolina
Apalachicola-Chattahoochee-
Flint River Basin
Georgia
Investigate the Influence of Hydrogeologic Setting on Contaminant Fate
Eastern San Joaquin Valley
California
Unsaturated Zone
Thin Thick
Oxic Zone
In
Ground Water
ThinNorth
Carolina------
Thick GeorgiaWisconsin California
•Nitrate concentrations are high but limited to upper few meters.
•Downstream impacts are limited by denitrification.
North Carolina: Nitrate Concentrations and Fate
OxicNitrate ReducingIron Reducing
10 mg/L
<1 mg/L
0
2
4
6
8
10
12
14
0 10 20 30 40 50
Ground Water Age (years)
Nit
rate
(as
N),
N2
fro
m
den
itri
f., D
isso
lved
Oxy
gen
(m
g/L
)
0.01
0.10
1.00
10.00
Iro
n (
mg
/L) Iron
N2 from denitrification
Nitrate
Diss.Oxygen
Use of Residence Times to Understand Chemical Evolution of Ground Water
Low Nitrate, High Denitrification
High Nitrate, No Denitrification
Low Nitrate, Low Denitrification
Wisconsin: Nitrate Concentrations and Fate
•High nitrate concentrations in top 10 m of saturated thickness.•Oxic conditions suggest significant downstream impacts on ground water and streams likely.
Oxic 8 mg/L8 mg/L
Larger Oxic Zone at Wisconsin Site is Due to Slower O2 Consumption Rates than at NC Site
0
2
4
6
8
10
0 10 20 30 40 50
Ground Water Age (years)
Dis
solv
ed O
xyge
n (m
g/L)
Wisconsin
North Carolina
0
2
4
6
8
0 10 20 30 40 50
Ground Water Age (years)
Dis
solv
ed O
2
Co
nsu
mp
tio
n (
mg
/L) NC: 0.36 mg O2/L per yr
WI: 0.18 mg O2/L
per yr
0
2
4
6
8
10
12
14
10 20 30 40 50 60
Recharge Nitrate Concentrations Increase From 1960 to 2000
1
10
100
10 20 30 40 50 60
Rec
har
ge
[NO
3- ] (m
g/L
as
N)
1950 1960 1970 1980 1990 2000
North Carolina
Note: 1) Independent variable in regression equations is years since 1940.
1950 1960 1970 1980 1990 2000
Wisconsin
R2=0.88 R2=0.33
Recharge Nitrate Concentrations =[NO3-]+[N2 from denitrification]
Rec
har
ge
[NO
3- ] (m
g/L
as
N)
Recharge Year Recharge Year
0
2
4
6
8
10
12
14
1950 1960 1970 1980 1990 2000
0
5
10
15
20
Nitrate Concentration Increases AreConsistent with Fertilizer and/or Manure Usage
1
10
100
1950 1960 1970 1980 1990 2000
0
5
10
15
20
25
30Wisconsin North Carolina
Nit
rog
en U
se (
kg
/acr
e)
Nit
rog
en U
se (
kg
/acr
e)
Fertilizer
Manure
[NO3-]
Rec
har
ge
[NO
3- ]
(mg
/L a
s N
)
Rec
har
ge
[NO
3- ]
(mg
/L a
s N
)
02468
101214
1950 1970 1990 2010
Nitrate Concentrations in Ground Water Explained by 30% of Fertilizer Applied
Wisconsin
30 % of applied N
Applied N dissolved in 21 cm of recharge applied to cropped area of county.
[NO3-]
in ground water
Rec
har
ge
[NO
3- ]
(mg
/L a
s N
)
Trends From This Study Agreewith Larger Spatial Study
1950 1960 1970 1980 1990 2000
Nit
rate
(m
g/L
as
N)
0
5
10
15
20
25
30
Land Use Study
Flow System Study
Pesticide Trends and Transformations
Relate atrazine concentrations to:
- crops planted in the county
- atrazine use rate Examine parent and degradate concentrations of
atrazine. Similar findings for metolachlor and alachlor and
their degradates.
Georgia: Land Use Changes Related to Increase and then Decrease in Atrazine + DEA?
1960 1970 1980 1990 2000
% o
f C
ou
nty
in C
orn
an
d S
oyb
ean
0
10
20
30
40
50
Atr
azin
e p
lus
Dee
thyl
atra
zin
e (
g/L
)
0.001
0.01
0.1
Atrazine+DEA
% Corn &Soybean
0.00
0.02
0.04
0.06
0.08
0.10
0.12
1950 1960 1970 1980 1990 2000
Atr
azin
e pl
us d
eeth
ylat
razi
ne
(g/
L)
0.0
0.5
1.0
1.5
2.0
2.5
3.0
Atr
azin
e U
se R
ate
(lbs
ai/a
cre)
AtrazineUse Rate
Atrazine + DEA
LocalLocalAtrazineAtrazineBanBan
Wisconsin:
-Atrazine or Deethylatrazine Found in All Samples
-Effects of Atrazine Ban Not Observed Yet
0 10 20 30 40 500.0
0.2
0.4
0.6
0.8
1.0
ACFB ALBE SANJ WMIC ALBE-AL
Ground Water Age (years)
Dee
thyl
atra
zin
e (D
EA
)M
ole
Fra
ctio
nDeethylatrazine Dominant at Sites with Thick Unsaturated
Zones but Not at Sites with Thin Unsaturated Zones-Suggests Degradation Occurs Primarily in the Unsaturated Zone
All Deethylatrazine
All Atrazine
DEA=Atrazine
Thick unsaturated zones
Thin unsaturated zones
Wisconsin California
North Carolina
Georgia
Summary
Coupling age dating with water chemistry data improves our understanding of:
•The Linkage Between Land Use Practices
and Water Quality
•Trends in Constituent Concentrations
•Transformation Rates of Constituents
Contact Information
Jim Tesoriero: [email protected] Karen Burow: [email protected] David Saad: [email protected] Elizabeth Frick: [email protected] Larry Puckett: [email protected]