measuring and monitoring systemssymposium.greenleafadvisors.net/wp-content/uploads/2015/... ·...
TRANSCRIPT
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Measuring and Monitoring Systems
Andy Ward, OSU Kevin King, USDA-ARS
Brittany Hanrahan and Sheila Christopher, University of Notre Dame
Laura Christianson, University of Illinois Jessica D’Ambrosio, Antioch College
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SERA-46 and Hypoxia Task Force
Objective 1: Establish and strengthen relationships that can serve the missions of multiple organizations addressing nutrient movement and environmental quality.
Objective 2: Expand the knowledge base through the discovery of new tools and practices as well as the continual validation of recommended practices.
Objective 3: Improve the coordination and delivering of educational programming and increase the implementation effectiveness of nutrient management strategies that reduce nutrient movement for agricultural and non-agricultural audiences.
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Monitoring, Calibration and Validation
• Determine the potential for use of comparable edge of field monitoring measures from state to state.
• Building from the work by the
Monitoring Collaborative, identify further gaps in data available.
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• Conduct a survey of experts within the 12 state region and other regions to determine: What data are needed at different scales Where will it come from How will it be used What will be the data security, confidentiality and ownership Who will do the data collection What will it cost and how will it be funded What data is already being obtained How is it being used
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Monitoring Surface Runoff and Tile Drainage Using Automated and Passive Sampling
Kevin King USDA-ARS
Soil Drainage Research Unit Columbus, OH
Healthy Soils for Healthy Waters; Memphis, TN: December 1, 2015
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Edge-of-field research
40 fields (20 paired fields)
representative of Ohio crop
production agriculture
Surface runoff and tile
discharge measurements
Using a before-after control-
impact study design
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Edge-of-field instrumentation
H-flumes for surface runoff
Thel-mar compound weirs and Isco area velocity sensors for tile
Automated samplers Year round sampling
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Uncertainty in phosphorus loads from
tile-drained landscapes
Mark Williams1
Kevin King1, Merrin Macrae2, Bill Ford3, Chris Van Esbroeck2, Richard
Brunke4, Michael English5, and Sherry Schiff2
1USDA-ARS – Columbus, OH 2University of Waterloo – Waterloo, ON 3Marshall University – Huntington, WV 4Ontario Ministry of Agriculture, Food, & Rural Affairs – London, ON 5Wilfrid Laurier University – Waterloo, ON
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Objectives
Quantify uncertainty in annual DRP load from tile-drained fields
and headwater watersheds resulting from infrequent sampling and
load calculation method
Compare uncertainty estimates from tile-drained landscapes to
naturally drained landscapes
Examine the impact of three compositing strategies on load estimates
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6 tile-drained study sites 2 headwater watersheds
(279 and 389 ha)
4 agricultural fields
(8 to 14 ha)
10 to 30 minute discharge
measurement
2 hour to 1 day sampling
frequency for DRP
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Ho
url
y v
olu
mtr
ic d
isch
arg
e (
mm
)
W1 W2 TD1 TD2 TD3 TD4
DR
P c
on
c.
(mg
L-1
)
1e+0
1e-1
1e-2
1e-3
1e-4
1e-5
1e+0
1e-1
1e-2
1e-3
1e-4
Study site
Discharge and DRP concentration
Date
Dis
ch
arg
e (
L s
-1)
0
10
20
30
40
50
DR
P c
on
c.
(mg
L-1
)
0.0
0.2
0.3
0.5
0.6
0.8
0.9
Discharge
DRP
3/07 3/21 4/04 4/18 5/02 5/16
DRP concentration increased with
discharge, but weak concentration-
discharge relationships were
observed for all sites (R2 < 0.10)
DRP concentration ranged from
0.001 to 1.69 mg L-1
TD2
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Sampling scenarios
3 compositing strategies were also tested:
1. Hourly samples (3, 6, or 12 h) were composited into a 1 d sample
2. Daily samples were composited every 2, 3, or 7 d
3. Hourly samples (6 h) were composited every 2, 3, or 7 d
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Selecting a sampling strategy
Continuous discharge measurements are a must
Uncertainty increases as sample frequency decreases regardless of
load estimation algorithm
For monitoring programs evaluating relative changes in load (e.g., %
change due to a change in management practice), precision is important
- Linear interpolation of concentrations (M6) offers a good
balance between accuracy and precision in tile-drained
landscapes
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Conclusions
The frequency of sampling, the algorithm used to estimate load, and
sample compositing introduce varying levels of uncertainty
For tile-drained landscapes –
To be within ±10% of reference DRP loads samples should be
collected every 13 to 26 h
Continuous discharge measurements and linear interpolation of
DRP concentration yielded the best balance between accuracy
and precision
Compositing samples generally decreases accuracy, but
increases precision of annual DRP load estimates
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How to know about the flow below where we grow: Monitoring nutrients in tile drainage DR. LAURA CHRISTIANSON
UNIVERSITY OF ILLINOIS AT URBANA -CHAMPAIGN
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Do we need both concentration and flow? Example: woodchip bioreactor
Photo Credit: Iowa Soybean Association/L. Christianson
≈20% concentration reduction
100% concentration reduction
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Options for tile water quality monitoring
Water chemistry (nutrient concentration): ◦ Grab sampling
◦ Autosampler
◦ Composite sampling permanent infrastructure
◦ Continuous, real-time sensors
Flow monitoring (flow volume/rate): ◦ Pressure transducer
◦ Area velocity meter
◦ Flow meter (pumped system)
http://conservationbytes.com/2009/04/15/cartoon-guide-to-biodiversity-loss-iv/
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Water chemistry: Tile water sampling Grab sampling: simplest method, little training required
◦ But you don’t know what is happening between samples
◦ Need to interpolate between samples
Autosampling for: ◦ Time-based samples
◦ Flow-based samples ◦ Composite samples (flow
proportional)
Use real-time sensors and sondes
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How often do I need to sample?
The probability of estimating the
annual mass loss within ±15% of the
“true” value:
◦ For weekly sampling: 92%;
◦ For monthly (30–day) sampling: 68%
◦ for 90–day frequency: 51%
95% confidence intervals of mass loss
estimates vs. “true” mass losses for different sampling frequencies
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Program to collect samples: ◦ based on flow,
◦ based on time, or
◦ composite
Electricity or battery powered
Maintenance: battery level, solar panel output, sample lines, desiccant, stage/recorder accuracy…
Keep lines clean, prevent from freezing
Example autosamplers
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Flow monitoring – Pressure Transducer
A V-notch weir is preferable to a rectangular weir
Must use a calibrated equation to calculate flow rate
Corrected for barometric pressure
𝑭𝒍𝒐𝒘 𝒓𝒂𝒕𝒆 𝒐𝒗𝒆𝒓 𝒕𝒉𝒆 𝑽
= 4.28 ∗ 𝐶𝑜𝑒𝑓𝑓𝑖𝑐𝑖𝑒𝑛𝑡
∗ tan𝐴𝑛𝑔𝑙𝑒 𝑜𝑓 𝑉
2
∗ 𝑑𝑒𝑝𝑡ℎ 𝑜𝑓 𝑤𝑎𝑡𝑒𝑟+ 𝐶𝑜𝑟𝑟𝑒𝑐𝑡𝑖𝑜𝑛 𝑓𝑎𝑐𝑡𝑜𝑟 2.5
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Drawing: Lawlor et al., 2008; Photos: M. Helmers, Iowa State Univ.
Plot-scale research: Permanent sumps
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Selecting a monitoring system: What matters to you? • Cost: What are the initial capital and ongoing maintenance costs?
Does funding fluctuate over time?
• Labor: Who will collect samples and maintain the equipment? What level of training do they need?
• Scientific Robustness: Are peer-reviewed publication quality data required?
• Site Details: Is electricity available? Is it a private farm or a research farm?
• Research question: Will nitrogen or phosphorus be monitored (or both)? Will plots be separated (e.g., using guard tiles or impermeable liners)?
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MONITORING AGRICULTURAL DITCHES
JESS ICA D’AMBROSIO
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U.S. CLEAN WATER ACT
• Chemical Integrity: • Water quality tests
(e.g., pH, dissolved oxygen, phosphorus, nitrogen)
• Formerly related to point sources (e.g., wastewater treatment plant effluent, power plant effluent)
• Physical Integrity: • Shape, form, physical
processes
• Largely relates to hydrology: how water flows across the land surface
• Geomorphology/ habitat
• Biotic Integrity: • Refers to ecology: how
does the ecosystem function compared to prior to development?
• Perhaps better at identifying non-point sources: biotic populations (i.e., fish, invertebrates, algae, birds, etc.) show cumulative/synergistic effects of anthropogenic impacts
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MONITORING HABITAT
• Ohio EPA method for evaluating habitat quality.
• Relies on observational (qualitative) or semi-quantitative measures.
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MONITORING FISH
• Ohio EPA has developed Ohio-specific IBI metrics & scoring.
• Ohio EPA also publishes lists of tolerant/intolerant classifications for all common Ohio fish species.
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MONITORING MACROINVERTEBRATES
http://www.plpt-waterquality.net/monitor/bioassess/bigmouthcancr.html
• Occupy middle of the food web.
• Now have fairly solid methods to identify to species, along with extensive environmental/pollution tolerance information.
• Evaluated using the Invertebrate Community Index (ICI) or Benthic Index of Biotic Integrity (B-IBI).
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MONITORING WATER QUALITY flow
• Linking continuous measurements
with sediment & nutrient export.
– Before-After-Control-Impact (BACI)
• Sampling: – Continuous turbidity & depth
measurements (every 30 min)
– Periodic surface water sampling
– Seasonal denitrification transects
– Rhodamine dye tracer tests
– P-filters on tile outlets