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Historical Analysis of
Agroenvironmental Conditions in
the Lower Mississippi River Basin
Lindsey Yasarer, Jason Taylor, J.R. Rigby, Martin Locke
USDA-ARS, National Sedimentation Laboratory, Oxford, MS
USDA-ARS Long-Term Agroecosystem
Research (LTAR) Network
Partnership among 18 long-term
research sites across the US.
Vision for LTAR Network:
“Transdisciplinary science conducted
over decades on the land in different
regions, geographically scalable,
enhancing the sustainability of agro-
ecosystem goods and services.”
(Walbridge and Shafer, 2011)
Lower Mississippi River Basin LTARhttp://www.tucson.ars.ag.gov/ltar/
LTAR Research Questions
1. What factors drive agricultural productivity and its environmental impacts?
2. What are the tradeoffs between productivity, quality, societal preferences, and
ecosystem services?
3. What are the barriers to sustainable intensification?
4. How do we better target our use of resources?
5. What technologies and management strategies are needed for agriculture to be
resilient to extreme events (e.g., weather, disease outbreaks, pest infestations)?
6. What scientific synthesis products are needed for decision making?
http://www.tucson.ars.ag.gov/ltar/
Ecosystem Services and Agriculture
Services provided by
agriculture beyond
food, fuel and fiber
Potential disservices
caused by intensive
cropland management
Foley et al. 2005. Global Consequences of Land Use. Science 309, 570.
Lower Mississippi River
Basin LTAR
• HUC 2 watershed
• Two dominant ecoregions
o Southeastern USA Plains
o Mississippi Alluvial and Southeast USA
Coastal Plains
Study the past if you want to define the future
~ Confucious
Study Goals:
1. Examine long-term trends in natural resources and environmental impacts of
managed agricultural systems
2. Evaluate historical data available in the LMRB to elucidate trends
o Agricultural census data
o Land-use records and geospatial datasets
o Precipitation records
o Hydrology and water quality data
Land-use in LMRB
2008 -2016
0
10000
20000
30000
40000
50000
60000
70000
80000
Corn
Cotton
Rice
Sorghum
Soybeans
WinterWheat
OtherCrops
Fallow/Idle
ForestAll
Var.Aquatic
Developed
Grass/Pasture
Shrubland
Area(km2)
2008 2016
Data from USDA Cropland Data Layers:
2008, 2012, 2016
+34%
+12%
-23%
-47%
Management Trend: Increase in irrigated
land-use
PERMITTED WATER USE LOCATIONS, MS GROUNDWATER USE IN ARKANSAS
COUNTY
Of 3,000,000 acres farmed, 2,000,000 are irrigated in
Delta (YMD)
USGS (2002)
Dominant Water Resource:
Mississippi River Valley Alluvial Aquifer
• Withdrawals of 9290 Million gallons per day
mainly for irrigation
•Ranked 3rd in the nation of total withdrawals
Maupin and Barber. 2000. Estimated Withdrawals from Principal Aquifers in the United States. USGS Circular 1279
Research Questions & Preliminary Methods
RESEARCH QUESTIONS
o Is there significant hydrologic
alteration detected at LMRB long-
term hydrologic gauges?
o How does degree of hydrologic
alteration vary between agricultural
and non-agricultural watersheds?
METHOD
o Use Indicators of Hydrologic
Alteration (IHA) software to
evaluate trends using both a time
series analysis and a change point
analysis (1990)
Indicators of Hydrologic Alteration (IHA)
o Developed by The Nature Conservancy (version 7.1)
o Examine hydrologic impacts of human activities; develop
environmental flow recommendations; analyze scenarios
o Requires at least 20 years of daily hydrologic data
o Calculates 67 ecologically-relevant statistical parameters
- IHA parameters
- Environmental Flow Component parameters
In this study:
o Base flow index: 7-day minimum flow/mean flow for year
o Extreme Low Flows (frequency)
o Minimum (1-day, 3-day, 7-day)
Study Sites
Watershed Study Sites
Tennessee Watersheds
Agricultural Watershed:
• Loosahatchie River at
Arlington:
• 25% Row crop
• 38% Forest/Shrub
• 25% Pasture/Grass
Non-Agricultural Watershed:
• Hatchie River at Bolivar:
• 6% Row crop
• 64% Forest/Shrub
• 14% Pasture/Grass
HATCHIE RIVER LOOSAHATCHIE RIVER
Base Flow Index 1969 -2016 (1990 Breakpoint)
Upland Non-agricultural Upland Agricultural
HATCHIE RIVER LOOSAHATCHIE RIVER
Base Flow Index 1969 -2016
p=0.5
r2 = 0.0008
Slope = 0
p=0.5
r2 = 0.004
Slope = 0
Upland Non-agricultural Upland Agricultural
HATCHIE RIVER LOOSAHATCHIE RIVER
Frequency of Extreme Low Flows
p=0.5
r2 = 0.007
Slope = 0.0152
p=0.025
r2 = 0.13
Slope = -0.124
Upland Non-agricultural Upland Agricultural
Arkansas Watersheds
Agricultural Watersheds:
• Cache River at Egypt
• 69% Row Crop
• 15% Forest/Shrub
• L’Anguille River near Colt
• 70% Row Crop
Non-Agricultural Watersheds:
• Saline River near Rye
• 0% Row Crop
• 73% Forest/Shrub
• Ouachita River at Camden
• 0% Row Crop
• 74% Forest/Shrub
Base Flow
Index
1969 -2016
1990
Breakpoint
Arkansas
SALINE RIVER
OUACHITA RIVER
CACHE RIVER
LANGUILLE RIVER
Upland Non-agricultural Lowland agricultural
Base Flow Index 1969-2016
SALINE RIVER CACHE RIVER
UplandNon-agricultural Lowlandagricultural
p=0.5
r2 = 0.038
Slope = -0.0003
p=0.001
r2 = 0.42
Slope = -0.0012
Frequency of Extreme Low Flows
SALINE RIVER CACHE RIVER
Upland Non-agricultural Lowland agricultural
p=0.25
r2 = 0.062
Slope = 0.07
p=0.001
r2 = 0.36
Slope = 0.14
Louisiana Watersheds
Agricultural Watersheds:
• Boeuf River near Girard
• 68% Row Crop
• 13% Other Cropland
• Tensas River at Tendal
• 76% Row Crop
• 12% Water/Wetland
Non-Agricultural Watersheds:
• Comite River near Comite
• 1% Cropland
• 34% Water/Wetland
• 30% Pasture/Grass
• 29% Forest/Shrub
• Amite River near Denham
Springs
• 0% Cropland
• 46% Forest/Shrub
• 27% Water/Wetland
Base Flow
Index
1969 -2016
1990
Breakpoint
Louisiana
Upland Non-agricultural Lowland agricultural
AMITE RIVER
COMITE RIVER TENSAS RIVER
BOEUF RIVER
Base Flow Index 1969-2016
Upland Non-agricultural Lowland agricultural
p=0.5
r2 = 0.0069
Slope = 0.0004
p=0.001
r2 = 0.51
Slope = -0.0008
COMITE RIVER TENSAS RIVER
Frequency of Extreme Low Flows
Upland Non-agricultural Lowland agricultural
p=0.5
r2 = 0.0002
Slope = 0.0045
p=0.05
r2 = 0.09
Slope = 0.06
TENSAS RIVERCOMITE RIVER
Overview of Time Series Analysis 1969-2016
State Site Name Base
flow
Frequency
Extreme
Low Flows
TN Hatchie NS NS
AR Saline NS NS
AR Ouachita NS NS
LA Amite NS p=0.025
LA Comite NS NS
State Site Name Base
flow
Frequency
Extreme
Low Flows
TN Loosahatchie* NS
p=0.025
AR Cache
p=0.001 p=0.001
AR Languille
p=0.05
NS
LA Boeuf
p=0.001 p=0.001
LA Tensas
p=0.001 p=0.05
UplandNon-agriculturalWatersheds LowlandAgriculturalWatersheds
* Located in uplands with only 25% agriculture
Conclusions
 Evidence of hydrologic alteration related to base flow and low flow events in
lowland agricultural watersheds
 We hypothesize that intensive use of groundwater for irrigation in agricultural
watersheds has altered flow patterns in surface water systems; however, more careful
analysis of water use data is necessary.
Further exploration needed:
 Tradeoffs? Ecosystem services vs. hydrologic alteration
 Ecological impacts of hydrologic alteration
Lindsey Yasarer
Research Hydrologist
National Sedimentation Laboratory
USDA-ARS Oxford, MS
Lindsey.Yasarer@ars.usda.gov

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Historical Analysis of Agroenvironmental Conditions

  • 1. Historical Analysis of Agroenvironmental Conditions in the Lower Mississippi River Basin Lindsey Yasarer, Jason Taylor, J.R. Rigby, Martin Locke USDA-ARS, National Sedimentation Laboratory, Oxford, MS
  • 2. USDA-ARS Long-Term Agroecosystem Research (LTAR) Network Partnership among 18 long-term research sites across the US. Vision for LTAR Network: “Transdisciplinary science conducted over decades on the land in different regions, geographically scalable, enhancing the sustainability of agro- ecosystem goods and services.” (Walbridge and Shafer, 2011) Lower Mississippi River Basin LTARhttp://www.tucson.ars.ag.gov/ltar/
  • 3. LTAR Research Questions 1. What factors drive agricultural productivity and its environmental impacts? 2. What are the tradeoffs between productivity, quality, societal preferences, and ecosystem services? 3. What are the barriers to sustainable intensification? 4. How do we better target our use of resources? 5. What technologies and management strategies are needed for agriculture to be resilient to extreme events (e.g., weather, disease outbreaks, pest infestations)? 6. What scientific synthesis products are needed for decision making? http://www.tucson.ars.ag.gov/ltar/
  • 4. Ecosystem Services and Agriculture Services provided by agriculture beyond food, fuel and fiber Potential disservices caused by intensive cropland management Foley et al. 2005. Global Consequences of Land Use. Science 309, 570.
  • 5. Lower Mississippi River Basin LTAR • HUC 2 watershed • Two dominant ecoregions o Southeastern USA Plains o Mississippi Alluvial and Southeast USA Coastal Plains
  • 6. Study the past if you want to define the future ~ Confucious Study Goals: 1. Examine long-term trends in natural resources and environmental impacts of managed agricultural systems 2. Evaluate historical data available in the LMRB to elucidate trends o Agricultural census data o Land-use records and geospatial datasets o Precipitation records o Hydrology and water quality data
  • 7. Land-use in LMRB 2008 -2016 0 10000 20000 30000 40000 50000 60000 70000 80000 Corn Cotton Rice Sorghum Soybeans WinterWheat OtherCrops Fallow/Idle ForestAll Var.Aquatic Developed Grass/Pasture Shrubland Area(km2) 2008 2016 Data from USDA Cropland Data Layers: 2008, 2012, 2016 +34% +12% -23% -47%
  • 8. Management Trend: Increase in irrigated land-use PERMITTED WATER USE LOCATIONS, MS GROUNDWATER USE IN ARKANSAS COUNTY Of 3,000,000 acres farmed, 2,000,000 are irrigated in Delta (YMD) USGS (2002)
  • 9. Dominant Water Resource: Mississippi River Valley Alluvial Aquifer • Withdrawals of 9290 Million gallons per day mainly for irrigation •Ranked 3rd in the nation of total withdrawals Maupin and Barber. 2000. Estimated Withdrawals from Principal Aquifers in the United States. USGS Circular 1279
  • 10. Research Questions & Preliminary Methods RESEARCH QUESTIONS o Is there significant hydrologic alteration detected at LMRB long- term hydrologic gauges? o How does degree of hydrologic alteration vary between agricultural and non-agricultural watersheds? METHOD o Use Indicators of Hydrologic Alteration (IHA) software to evaluate trends using both a time series analysis and a change point analysis (1990)
  • 11. Indicators of Hydrologic Alteration (IHA) o Developed by The Nature Conservancy (version 7.1) o Examine hydrologic impacts of human activities; develop environmental flow recommendations; analyze scenarios o Requires at least 20 years of daily hydrologic data o Calculates 67 ecologically-relevant statistical parameters - IHA parameters - Environmental Flow Component parameters In this study: o Base flow index: 7-day minimum flow/mean flow for year o Extreme Low Flows (frequency) o Minimum (1-day, 3-day, 7-day)
  • 13. Tennessee Watersheds Agricultural Watershed: • Loosahatchie River at Arlington: • 25% Row crop • 38% Forest/Shrub • 25% Pasture/Grass Non-Agricultural Watershed: • Hatchie River at Bolivar: • 6% Row crop • 64% Forest/Shrub • 14% Pasture/Grass
  • 14. HATCHIE RIVER LOOSAHATCHIE RIVER Base Flow Index 1969 -2016 (1990 Breakpoint) Upland Non-agricultural Upland Agricultural
  • 15. HATCHIE RIVER LOOSAHATCHIE RIVER Base Flow Index 1969 -2016 p=0.5 r2 = 0.0008 Slope = 0 p=0.5 r2 = 0.004 Slope = 0 Upland Non-agricultural Upland Agricultural
  • 16. HATCHIE RIVER LOOSAHATCHIE RIVER Frequency of Extreme Low Flows p=0.5 r2 = 0.007 Slope = 0.0152 p=0.025 r2 = 0.13 Slope = -0.124 Upland Non-agricultural Upland Agricultural
  • 17. Arkansas Watersheds Agricultural Watersheds: • Cache River at Egypt • 69% Row Crop • 15% Forest/Shrub • L’Anguille River near Colt • 70% Row Crop Non-Agricultural Watersheds: • Saline River near Rye • 0% Row Crop • 73% Forest/Shrub • Ouachita River at Camden • 0% Row Crop • 74% Forest/Shrub
  • 18. Base Flow Index 1969 -2016 1990 Breakpoint Arkansas SALINE RIVER OUACHITA RIVER CACHE RIVER LANGUILLE RIVER Upland Non-agricultural Lowland agricultural
  • 19. Base Flow Index 1969-2016 SALINE RIVER CACHE RIVER UplandNon-agricultural Lowlandagricultural p=0.5 r2 = 0.038 Slope = -0.0003 p=0.001 r2 = 0.42 Slope = -0.0012
  • 20. Frequency of Extreme Low Flows SALINE RIVER CACHE RIVER Upland Non-agricultural Lowland agricultural p=0.25 r2 = 0.062 Slope = 0.07 p=0.001 r2 = 0.36 Slope = 0.14
  • 21. Louisiana Watersheds Agricultural Watersheds: • Boeuf River near Girard • 68% Row Crop • 13% Other Cropland • Tensas River at Tendal • 76% Row Crop • 12% Water/Wetland Non-Agricultural Watersheds: • Comite River near Comite • 1% Cropland • 34% Water/Wetland • 30% Pasture/Grass • 29% Forest/Shrub • Amite River near Denham Springs • 0% Cropland • 46% Forest/Shrub • 27% Water/Wetland
  • 22. Base Flow Index 1969 -2016 1990 Breakpoint Louisiana Upland Non-agricultural Lowland agricultural AMITE RIVER COMITE RIVER TENSAS RIVER BOEUF RIVER
  • 23. Base Flow Index 1969-2016 Upland Non-agricultural Lowland agricultural p=0.5 r2 = 0.0069 Slope = 0.0004 p=0.001 r2 = 0.51 Slope = -0.0008 COMITE RIVER TENSAS RIVER
  • 24. Frequency of Extreme Low Flows Upland Non-agricultural Lowland agricultural p=0.5 r2 = 0.0002 Slope = 0.0045 p=0.05 r2 = 0.09 Slope = 0.06 TENSAS RIVERCOMITE RIVER
  • 25. Overview of Time Series Analysis 1969-2016 State Site Name Base flow Frequency Extreme Low Flows TN Hatchie NS NS AR Saline NS NS AR Ouachita NS NS LA Amite NS p=0.025 LA Comite NS NS State Site Name Base flow Frequency Extreme Low Flows TN Loosahatchie* NS p=0.025 AR Cache p=0.001 p=0.001 AR Languille p=0.05 NS LA Boeuf p=0.001 p=0.001 LA Tensas p=0.001 p=0.05 UplandNon-agriculturalWatersheds LowlandAgriculturalWatersheds * Located in uplands with only 25% agriculture
  • 26. Conclusions  Evidence of hydrologic alteration related to base flow and low flow events in lowland agricultural watersheds  We hypothesize that intensive use of groundwater for irrigation in agricultural watersheds has altered flow patterns in surface water systems; however, more careful analysis of water use data is necessary. Further exploration needed:  Tradeoffs? Ecosystem services vs. hydrologic alteration  Ecological impacts of hydrologic alteration Lindsey Yasarer Research Hydrologist National Sedimentation Laboratory USDA-ARS Oxford, MS Lindsey.Yasarer@ars.usda.gov

Notes de l'éditeur

  1. 107,000 sq. miles over 5 states 85% is within the Mississippi Alluvial Plain and Southeastern Plains 40% of land area is agricultural land-use Humid Subtropical climate 1188 – 1617 mm precipitation
  2. First step is to begin exploring the data – this presentation will present some of the initial stages of this effort
  3. 98% of total withdrawals for irrigation; Arkansas represents 70% of the total Aquifer is source of 90% of irrigation water used in MS Delta Due to the intense use of groundwater for irrigation there have been noticeable changes in surface water systems and reduced connectivity between surface and groundwater
  4. Long-term records at USGS gauges in watersheds dominated by row crop land-use will have statistically significant indicators of hydrologic alterations in low flow conditions compared to gauges in other watersheds in the LMRB. (p<0.05)