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Watershed Diagnostics for Improved Adoption of
Management Practices: Integrating Biophysical and
Social Factors
PAUL T. LEISNHAMDEPT. ENVIRONMENTAL SCIENCE & TECHNOLOGY,
COLLEGE OF AGRICULTURE & NATURAL RESOURCES, UNIVERSITY OF MARYLAND
NIWQP: 2012-51130-20209; $631,500
Talk Outline1. Background
2. Impacts of climate change on pollution Critical Source Areas (CSAs)
3. Impacts of climate change on Best Management Practice (BMP) effectiveness
4. Competing views on water pollution and BMPs among stakeholders
Paul Leisnham, Socio-Ecology
Dan Boward, MD-DNREcology
Tom Hutson & Nicole Barth,Extension
David Lansing, UMBC
Sociology
Adel Shirmohammadi, Hydrology
Victoria Chanse, Amanda Rockler & numerous
studentsExtension & Sociology
Hubert Montas, Diagnostic Tools
Jaison Rekenberger, Diagnostic Tools
Daniel Schall,UMBC
Sociology
Julianna Brightman, Sociology
Develop, implement, and evaluate a cross-disciplinary approach for watershed management that considers
both technical (biophysical) and social factors
Objectives1. Evaluate community attitudes towards water resources and
identify barriers to BMP adoption2. Develop a Diagnostic Decision Support System (DDSS) to
identify CSAs and prescribe targeted BMPs3. Develop and evaluate strategies for increasing awareness and
behaviors towards water quality to increase BMP adoption
Tom Fisher, Horn Point Laboratory, UMCES
Algae and turbidity are increasing over time, and summer bottom DO is decreasing
Little improvement in Chesapeake Bay in past 40 years
0
0.2
0.4
0.6
0.8
1
1.2
5/1/87 5/6/87 5/11/87 5/16/87 5/21/87 5/26/87 5/31/87
Date
Prec
ipita
tion
(inch
es/d
ay)
Study Area Spatial Database
Pollutant Transport
ModelDiagnosis
Expert SystemPollutant Export Hot Spots BMP Allocation Plan
Prescription Expert SystemExcess Export Causes
Pollutant Hot Spots
Excess ExportCauses
Bio-Dynamic Models
DDSS Development
Components: GIS, Models, Expert Systems
Models: SWAT (SUSTAIN, AQUATOX, FIBI, EPA BASINS)
Expert Systems: MATLAB (predicate calculus to decision trees)
• DDSS will rank environmental causes to pollution and prescribe a BMP allocation plan
• Geo-referenced biophysical and land management data
• Simulate watershed
responses to selected stressors
• Identify CSAs & prescribe appropriate BMPs
• More “bang for the buck”
Climate Change Forecasts for the Northeastern United States↑ Elevated concentrations of atmospheric CO2
↑ Elevated mean temperature↑ Increased mean rainfall ↑ Shift in seasonal rainfall patterns
o Wetter springo Drier late summer
↑ Increases in extreme weather events
Climate Change: Precipitation ChangesPrecipitation Volume: Very Heavy Events i.e., top 1%
(1958-2012)
Model Construction and AnalysisSoftware Purpose and Progression
ArcGIS Spatial Data Analysis(Graphics and Database)
ArcSWAT Model developmentSWAT input file Generation
SWAT-CUP Model calibration(SUFI-2 Method)
SWAT Experimental engine(SWAT.exe)
Model Calibration Warm-up (3 yrs): 1/1/1990 to 12/31/1992 Calibration Period (15 yrs): 1/1/1990 to 12/31/2004
Data Type CharacteristicsTopography/DEM 10 meter
Landuse/Land Cover NLCD 2006 HRUSoils NRCS SSURGO
Weather (Calibration) 3 stations NCEP CFSR
Flow, Nutrients and Sediment
1 USGS Gauging Station Greensboro
Climate ChangeGFDL-CM2.1
CMIP3 (B1, A1B, A2)(Mid and End Century)
Model Validation Warm-up (2 yrs): 1/1/2005 to 12/31/2006 Validation Period (6 yrs): 1/1/2005 to
12/31/2010
Downscaled climate predictions from global model based around 3 IPCC scenarios that lead to low, medium, and high future levels of CO2
Definition of a Critical Source Area (CSA)
Rank SurQ (mm H20) TSS (tonnes/ha/yr) TN (kg/ha/yr) TP (kg/ha/yr)
Top 10% >406 >1.03 >24 >1.9
Top 20% >359 >0.73 >16 >1.6
Top 10%: Value for which the top ~770 HRUs is separated from the other 7705 HRUs
Top 20%: Value for which the top ~1540 HRUs is separated from the other 7705 HRUs
An area that exports a target pollutant at concentrations significantly above average
Always defined a watershed area (or HRU) a CSA if it exported a given pollutant at these fixed thresholds
Impacts of Climate Change on Pollution
CSAs
Watershed Response: Baseline and Climate Change Scenarios
B a se l i n e M i d C e n t u r y ( 2 0 4 6 - 2 0 6 4 )
E n d C e n t u r y ( 2 0 8 1 - 2 1 0 0 )
400450500550600650700750800850
B1 A1B A2
Stre
am fl
ow(m
m/y
r)
B a s e l i n e M i d C e n t u r y ( 2 0 4 6 -2 0 6 4 )
E n d C e n t u r y ( 2 0 8 1 -2 1 0 0 )
10
12
14
16
18
20
22
B1 A1B A2
tota
l nitr
ogen
(kg/
ha/y
r)
B a se l i n e M i d C e n t u r y ( 2 0 4 6 - 2 0 6 4 )
E n d C e n t u r y ( 2 0 8 1 - 2 1 0 0 )
0.7
0.8
0.9
1.0
1.1
1.2
1.3
1.4
1.5
B1 A1B A2
tota
l pho
spho
rus (
kg/
ha/y
r)
B a se l i n e M i d C e n t u r y ( 2 0 4 6 - 2 0 6 4 )
E n d C e n t u r y ( 2 0 8 1 - 2 1 0 0 )
0.4
0.5
0.6
0.7
0.8
0.9
1.0
1.1
B1 A1B A2
Sedi
men
t(M
g/ha
/yr)
Surface Run-off & Total Suspended Solids
Present Day CSAs SRES A2 End Century CSAs
25-30% ↑ rainfall
3.9X ↑ 3.0X ↑
Present Day CSAs SRES A2/A1B End Century CSAs
Nitrogen & Phosphorous
25-30% ↑ rainfall
3.7X ↑ 2.5X ↑
Impacts of Climate Change on BMP Effectiveness
Targeting Method: Dense CSAs𝐶𝑟𝑖𝑡𝑖𝑐𝑎𝑙𝑙𝑦 𝐷𝑒𝑛𝑠𝑒𝐴𝑟𝑒𝑎𝑠𝑎𝑡 h𝑡 𝑒𝑡𝑜𝑝 20% 𝐵𝑟𝑒𝑎𝑘𝑉𝑎𝑙𝑢𝑒
Rank SurQ (mm H20) TSS (tonnes/ha/yr) TN (kg/ha/yr) TP (kg/ha/yr)Top 10% >406 >1.03 >24 >1.9Top 20% >359 >0.73 >16 >1.6
Targeting Dense CSAs of TodayResidual CSA Density with Baseline BMP Design Subjected to Current, A1B and A2 Climate Conditions
TMDL targets met 64%-143% above TMDL Targets
Targeting Dense CSAs of the Future
Residual CSA Density with A2 BMP Design Subjected to Current, A1B and A2 Climate Conditions.
TMDL targets met TMDL targets met
Competing Views on Water Pollution &
Management Among Stakeholders
Two dominant discourses from Interviews and Q-sort
Scientists and environmental professionals: Stressed the role of agriculture in water degradation, & importance of regulating all adverse land-use practices
Farmers and agricultural extension agents: Stressed the importance of industry-driven regulation, local knowledge & were skeptical of “outside” knowledge, including science.
Axes of Regulation and Cultural Knowledge
Legend
Increasing Regulation
Deregulation
Outside knowledge
Local knowledge
Highlights Summary1. Climate change will likely increase areas that export
excessive levels of pollutants
2. Targeting CSAs works, but a BMP allocation plan based on today’s CSAs fail to meet TMDL goals
3. We need a BMP allocation plan based on future climate scenarios demanding greater community-based participation
4. We need to overcome existing divergent viewpoints among stakeholders on pollution and its management
Final Work: Integrating Social Dimensions into DDSS
KAP surveys with farmers and urban residents.
Example Research-Education-Extension Outputs
3 journal papers in press or advanced peer-reviewo 2 in Special Climate Change edition of Transactions of the ASABE
3 journal articles in prep.
12 presentations at national conferenceso Best student poster (Renkenberger) at 2014 AWRA Annual Meeting
2 MS students graduated
6 undergraduates trained
Graduate class developed (“Watershed Ecosystem Sustainability”)
4-H EcoStewards program developed (850 participants)o 4-H youth and adult water quality education aids
Adult water quality in-service trainings for educators (190 participants)
Extra Slides
Extension Outreach
Interested Not interested020406080
59
12
Farmer interest of additional in-formation on BMPs (n=71)
Interest
Num
ber o
f far
mer
s
Improving awareness Leveraging connections with trusted knowledge sources (Extension & State agencies)
4-H youth programs County fair exhibits Town-hall meetings
Extension Outreach
Pamphet Youtube Workshop Extension Govt Other0102030405060
12
2
14
40
19
3
29
5
20
57
42
3
BMP information delivery of 59 re-spondent farmers
'Existing Delivery (n=90)'Desired Delivery (n=156)
Delivery Method
Num
ber o
f res
pons
es
Interested Not interested0
20406080
59
12
Farmer interest of additional information on BMPs (n=71)
Interest
Num
ber o
f far
mer
s
Polarizing statements
There is very strong evidence that agriculture is the single largest source of nitrogen, phosphorous and sediment going into the Chesapeake Bay.
Water problems like Pfiesteria should not be blamed on chicken manure because of all of the sewage being pumped into the bay right in the port of Baltimore. Pollutants like this in the bay aren’t from the farmers.
The most effective regulators are people who came up from the industry of whatever it is they’re regulating because they understand what actually happens.
Large companies like Perdue control all aspects of growing chickens, they should pay for Agricultural Best Management Practices for farmers.
1 2 3 4
Water problems like Pfiesteria should not be blamed on chicken...
The most effective regulators are people that come up from industry...
There is very strong evidence that agriculture is the single largest source of nitrogen...
Large companies like Perdue control all aspects of growing chickens...
Strongly Disagree
Disagree Agree Strongly Agree
Farmer (n = 66)
responses as part of survey
These statements stimulated the strongest responses and were the most polarizing, from 26
stakeholder interviews and Q-sort analysis
Paired T-TEST: T = -11.60, p < 0.0001
Biophysical ModelingOnce we have a working model…
1. We can use best available science to find Critical Source Areas (CSAs)
2. We don’t have to physically install BMPs (now or in the future), saving money
3. We can use the model to test BMP configurations that will achieve TMDL targets
Effects of Climate Change
B1
A2A1B
SWAT(Soil Water and
Assessment Tool)
Land Use/CoverTopography
SoilsWeather
Other
Flow PredictionSediment LoadingsNutrient Loadings
Water Balance/Availability Nutrient Output x BMP Removal Eff (%) = TMDL Attainment
BMP Design and Targeting MethodsTypical Design
StrategyBaseline Model
(SWAT)
Apply targeting method and calculate BMP efficiencies
Repeat for A2 and A1B scenarios using baseline
conditions
Future Proof Design Strategy
End Century Model(SRES A2 SWAT)
Apply targeting method and calculate BMP efficiencies
Repeat for Baseline and A1B scenarios using A2 conditions
Examine effect of climate change on BMP implementation
Compare/Evaluate Two Targeting Methods:• CSA Based (Dense CSAs)• Non-CSA Based (Land Use)
Apply Generic SWAT BMP
Removal Required to Meet Bay TMDL Targets
Scenario TSS TN TP
Baseline 33% 45% 23%B1 63% 64% 49%
A1B 69% 70% 53%A2 71% 67% 57%
Results: In-Stream Validation, MonthlyPoints falling on SWAT generated
streams were correlated by month
1.Reach Export Correlation◦ Discharge is significant in the same month as
well as the month prior◦ TP is significant in the same month of
sampling◦ TSS and TN are significant in month prior to
sampling
2. Two month lag was considered but may be anomalous due to infrequent sampling
Constituent IBI (%) Habitat Index (%)Month Discharge (cm/s) -0.83 -0.86 Sediment (mg/L) 0.38 -0.16 Total N (mg/L) 0.80 0.35 Total P (mg/L) -0.83 -0.52
Month-1 Discharge (cm/s) -0.79 -0.98 Sediment (mg/L) -0.60 -0.67 Total N (mg/L) -0.32 -0.66 Total P (mg/L) 0.05 0.52
Month-2 Discharge (cm/s) -0.12 -0.19 Sediment (mg/L) 0.20 -0.36 Total N (mg/L) 0.82 0.39 Total P (mg/L) -0.91 -0.58
Point Sources + Non-Point Sources + Margin of Safety
Motivation: EO 13508 and Regulation
TSS, TN and TP