technology session 1: assessing and evaluating ecosystem … · 2009-10-05 · outline sensor...
TRANSCRIPT
Tom HarmonEnvironmental Systems Grad Program
Sierra Nevada Research InstituteUniversity of California, Merced
& UCLA Center for Embedded Networked Sensing (CENS)
National Science FoundationFunding: Center for Embedded Networked Sensing, WATERS Network Design Team, Pan-American Advanced Studies Institute
Technology Session 1: Assessing and Evaluating Ecosystem Function
Precision Sustainability…
• Precision Agriculture: Using technology to enable adding precise amounts of water, fertilizer, pesticides to minimize costs while maximizing crop yield
• Precision Sustainability: Using technology to enable precise management of water from the perspectives of municipal, industrial, agricultural, and environmental needs
Outline Sensor Systems (remote + embedded)
What is possible now and in the near future? How do we assess aquatic and terrestrial
ecosystem functions more efficiently? Multi-scale assessment technologies (Integrated
Sensor-Model Systems) How do we evaluate ecosystem function in the
context of human well-being as objectively aspossible? Participatory sensing (enabling the citizen scientist)
Remote sensing (satellites)
Current Capabilities of Earth Observing Satellites
Spatial: 0.6 to 4 m10 to 30 m100 to 500 m1 to 8 km
Temporal: 0.5 hrDailyWeeklyBimonthly
Spectral: Panchromatic (1)Multispectral (2-6)Hyperspectral (10s-100s)
example: evapotranspiration potential forecasted using hourly GOES and MODIS and calibrated using weather station data(courtesy of Susan Ustin, UC Davis)
Remote Sensing and Water Quality• Aircraft-based
multispectral imaging to achieve necessary spatial resolution
• Turbidity, TSS, chlorophyll-a, CDOM
• There is more potential here
Brezonik and co-workersSee: http://water.umn.edu/pres_pubs.html
Other air/ground-based remote sensing
• Lidar – high resolution DEM, vegetation topology, snow/ice cover
• Thermal infrared remote sensing – thermal gradients, mixing phenomena, pollution sources
• CUAHSI Hydrologic Measurement Facility (http://www.cuahsi.org/hmf.html)
– Geophysical: electromagnetic toolbox (em induction, ground-penetrating radar, electrical resisitivity imaging)
– Evapotranspiration Suite• Integrated Cavity Output Spectroscopy (ICOS)
– water vapor isotopes for quantifying and partitioning large scale ET fluxes
• Large Aperture Scintillometer (LAS) – large-scale sensible heat fluxes, atmospheric turbulence
• Codar – HF radar – large scale surface water velocity, wave action
Source: John JensenU South Carolina
Bonner, Maidment, Minsker, et al.WATERS Test Bed Site at
Corpus Christi Bay
Ground-based Sensors Status and Outlook
Physical Sensors…increasingly smaller, cheaper
Chemical Sensors: gross concentrations, changes
Acoustic and Image data samples
Acoustic, Image sensors with on board analysis
Chemical Sensors: trace concentrations, universal sensors
(lab-on-a-chip)
DNA microarrays onboard embedded device, universal sensors
Sensor triggered sample collection (bridging technology)
present future
Organism tagging, tracking
ab
ioti
cb
ioti
c
DNA biosensors for targeted microorganism
Physical Sensors
ParameterField-Readiness Scalability Cost
Temperature High High 50–100Moisture Content High High 100–500Flow rate, Flow velocity High Medium–High 1,000–10,000Pressure High High 500–1,000Light Transmission (Turbidity) High High 800–2,000
Goldman et al. (2007) White Paper
ChemicalSensors
ParameterField-
Readiness Scalability Cost ($)Dissolved Oxygen High High 800–2,000Electrical Conductivity High High 800–2,000pH High High 300–500Oxidation Reduction Potential Medium High 300–500Major Ionic Species (Cl-, Na+) Low–Medium High 500–800Nutrients (Nitrate, Ammonium) Low–Medium Low–High 500–25000Heavy metals Low Low NASmall Organic Compounds Low Low NALarge Organic Compounds Low Low NA
Scalable nitrate sensor fabrication efforts
7 µm diam. carbon fiber-based nitrate
microsensor
Bendikov et al. Sensors and Actuators B: Chemical (2005; 2007)
Allen et al. Bioscience 57(10) (2007)“Soil Sensor Technology: Life within a Pixel”
Biosensors• Not field-ready sensors for
direct observations of key organisms (e.g, pathogens)
• Flow-thru instruments:– FlowCAM: phytoplankton, etc.
by image recognition
• Surrogates– Fluorescence (Chlorophyll,
CDOM, etc.) images from:Fluid Imaging Technologies
Much activity in basic sensor development!• e.g., Chemical Reviews special issue Feb 2008
– Optical Chemical Sensors, McDonagh et al. [288 refs]– Potentiometric Ion Sensors, Bobacka et al. [324 refs]– Chemical Sensors with Integrated Circuits, Joo and Brown [115 refs]– Surface Plasmon Resonance Sensors … Chemical and Biological Species,
Homola [335 refs]– DNS Biosensors and Microarrays, Sassolas et al. [444 refs]
McDonagh et al. Chemical Reviews, 2008, 108(2)
DNA/Biosensor exampleDNA detection utilizing a chrono-coulometric detection method
Redox-cycling current is detected at the electrodes over time – when labeled target DNA is hybridized with the probe DNA, current change occurs
Schienle et al. IEEE J. Solid-State Circ. (2004)
chip dimensions: 6.4 x 4.5 mm
publications for DNAbiosensors and
microarrays
Sassolas et al. Chemical Reviews (2008)
Embedded Sensor Systems• Arrays of static sensors
– Continuous in time, nested in space– Fusion with intermittent remote sensing
data– Aggregate signal is higher order
information than that form individual sensors (e.g., ET sensor suite)
• Mobile sensors– Continuous in space, periodic or event-
triggered in time– Fusion with static and remote sensing
data– Calibration for multidimensional fluid
dynamic models• Human in-the-loop mobile sensors
– Campaign-driven (periodic or event-driven)
– Synergize with educational aspects– Collect social science data
simultaneously
A. Sanderson, RPI
W. Kaiser, CENS-UCLA
T. Harmon, CENS-Merced
Outline Sensor Systems (remote + embedded)
What is possible now and in the near future? How do we assess aquatic and terrestrial
ecosystem functions more efficiently? Multi-scale assessment technologies (Integrated
Sensor-Model Systems) How do we evaluate ecosystem function in the
context of human well-being as objectively aspossible? Participatory sensing (enabling the citizen scientist)
Understanding and assessing ecosystems & their functions
• Plan to observe
• Observe
• Analyze data (e.g. test your models)
• Modify observation plan
• Observe more
• Analyze more data
• Repeat until you’re finished or (more likely) out of time
• Plan to observe• Observe• Analyze data (e.g. test your models)• Modify observation plan• Observe more• Analyze more data• Repeat until you’re finished or (more likely) out of time
We must learn to compress the timeline for this process
How? Multi-scale Observations• Multi-scale observatories
– Remote sensing + on-the-ground sensing– Integrated with models
• The total information is greater than the sum of the sensor data!– Systems of sensors become “virtual sensors” for higher order
information
• Provides 25% of US agriculture production, most from just three counties (based on $)
• Soil salinization trajectory shows lack of sustainability (decades timescale)
• Population growth, urbanization, climate change on top of this…
“The sustainability of irrigated agriculture in many arid and semiarid areas of the world is at risk because of a combination of several interrelated factors, including lack of fresh water, lack of drainage, the presence of high water tables, and salinization of soil and groundwater resources.”
Schoups et al. (2005), Proc. National Academy of Sciences, vol. 102 no. 43.
Example 1: Salinity and observation and management in a watershed Soil Salinization
San Joaquin Valley, CA
Agricultural drainage on San Joaquin River, CA
• Provides 25% of US agriculture production, most from just three counties (based on $)
• Soil salinization trajectory shows lack of sustainability (decades timescale)
• Population growth, urbanization, climate change on top of this…
Example 1: Salinity and observation and management in a watershed Soil Salinization
San Joaquin Valley, CA
Agricultural drainage on San Joaquin River, CA
“Nowhere in the United States are these issues more apparent than in the San Joaquin Valley of California.”
Schoups et al. (2005), Proc. National Academy of Sciences, vol. 102 no. 43.
Backbone observation efforts in place
Salt Slough
Mud Slough
SJR near Vernalis
Stanislaus River
Tuolumne River
Merced River
Courtesy of Nigel QuinnLawrence Berkeley National Lab & USBR
California Digital Exchange Center (CDEC):
- Hydrologic database- Some parts real-time- Some water quality sensors (EC, temp)
- Spatially sparse (10s of km granularity)
Studies on the Merced River
watershed
Mixing zone study:Merced-San Joaquin confluence(Harmon, Kaiser et al.)
Dairy manure application study (Harmon, Castillo et al)
USGS/NAWQA agricultural gw-sw flow path site(USGS and UCM)
Sierra Nevada Hydrologic Observatory (Bales et al)
Wetlands salinity management sites (Quinn, Harmon et al.)
Mine tailings and habitat restoration (Dunne et al. UCSB)
Lower Merced River Dairy Sensor System
Manure lagoon
• Production dairies large part of Central California• How to make dairy operations sustainable?• OBJECTIVE: To observe, understand, and manage the application of manure as fertilizer [and how is it connected to groundwater and the river?]
Sensor and Data Acquisition Hardware
• Off-the-shelf:– Moisture– Temperature– Soil salinity– Meteorology– Nitrate– Ammonium
• also some developmental nitrate sensors
Deploy forMonths to
years
Deploy fordays
Data-logger with radio or
cellular modem
Irrigation events
Salinity eventually carried to depth by water
For soil salinity:
• Observed patterns are as expected
• Simulation models are mature for flow, chemical, and energy transport in soils
• So, we can automate analysis
• In fact, for agricultural and engineered systems, we can use sensor feedback and models to control the system (precision agriculture or precision sustainability
Precision Agriculture with Reclaimed Water
• Palmdale water reuse experimental site (not in the SJV, but could be…)
• Microclimate + soil pylons (moisture, temp, short-term nitrate and ammonium)
• sensor feedback, model calibration, model forecast
• Receding horizon control (look ahead multiple management steps)
Soil
moi
stur
e (c
m3 /c
m3 )
Management step 40.245
0.24
0.235
0.23
0.225
0.22
0.215
0.21
time (min)0 5 10 15 20 25 30
estimatedmeasuredestimatedmeasured
time (min)
estimatedmeasuredestimatedmeasured
Management step 30.225
0.22
0.215
0.21 0 5 10 15 20 25 30
Soil
moi
stur
e (c
m3 /c
m3 )
Studies on the Merced River
watershed
Mixing zone study:Merced-San Joaquin confluence(Harmon, Kaiser et al.)
Dairy manure application study (Harmon, Castillo et al)
USGS/NAWQA agricultural gw-sw flow path site(USGS and UCM)
Sierra Nevada Hydrologic Observatory (Bales et al)
Wetlands salinity management sites (Quinn, Harmon et al.)
Mine tailings and habitat restoration (Dunne et al. UCSB)
Wetland Ecosystem Functions(here, a heavily managed ecosystem)
Grasslands Ecological Area, Central California
Patrick Rahilly 2008 MS Thesis (UC Merced)
Wetlands Project Overview
• Study the effects of delaying the seasonal release of pond water (it is warmer and saltier, but the river flow is higher and able to dilute it)
• Assess the impact of the change on wetland plant ecology (mostly for the benefit of the wildfowl populations)
Objectives
Multi-scale sensing system• Remote sensing: high resolution aerial imagery (RBG and near-infrared)
• Human-in-the-loop sensing: electro-magnetic scanning of soil (moisture, salinity)
• Embedded sensing: meteorology, soil moisture, temperature, salinity
Transects walked 15m apart auto sampling every 4m
Soil salinity mapping methods
Trimble Ag114
Geonics EM-38 MK1
Typical results: plant productivity, soil salinity, micro-topography (not shown)
TWO (2) SETS OF FALSE COLOR COMPOSITE AERIAL PHOTOGRAPHS TAKEN
…MAY 11, 2006 & …JUNE 09, 2006
PROJECT DESCRIPTION
Key plant species correlates with aerial imagery product (as long as you time the flyover well)
NDVI is a common veg index based on near infrared band
So far, we see signs that the delayed drawdown may alter plant ecology, but we are repeating in 2008 to be certain and to clarify the role of salinity
Studies on the Merced River
watershed
Mixing zone study:Merced-San Joaquin confluence(Harmon, Kaiser et al.)
Dairy manure application study (Harmon, Castillo et al)
USGS/NAWQA agricultural gw-sw flow path site(USGS and UCM)
Sierra Nevada Hydrologic Observatory (Bales et al)
Wetlands salinity management sites (Quinn, Harmon et al.)
Mine tailings and habitat restoration (Dunne et al. UCSB)
Example Application: San Joaquin-Merced Confluence Tests (2005-2007)
Sensor System:• Networked Info-mechanical
system (NIMS), a 2D robotic system
• Can carry ADP, water quality sondes, water sampling system
Objectives:• Cross-sectional velocity
fields (informing models, sediment transport, geomorphology)
• Gradient mapping– Flow adjustment to
optimize mixing, reaeration (reservoir operation)
• Mass balances over river sections, reaches– Groundwater loss/gain– Chemical fluxes from
groundwater
2007 Mass balance and mixing study
The bottom of the watershed at the San Joaquin confluence
San Joaquin-Merced River Confluence
55 m span NIMS RD- Sontek ADV- Hydrolab sonde- 1 low res scan- 2 high res scans
NIMS 2D river scanning system (for relatively low energy flow, < 1 m/s)
Coupled velocity-conductance readings(integrated to yield a total salt load)
Day 2:9.33 kg/s
Day 1:9.30 kg/s
Harmon et al. Environ. Eng. Science,24(2), 2007
San Joaquin side Merced side
Salinity gradient and integrated salt load in the mixing zone
Other quick examples in terrestrial ecology
Phil Rundel, William Kaiser, UCLA; Mike Allen, UC Riverside, Michael Hamilton, UC Blue Oaks Reserve, Eric Graham CENS, Tom Harmon, UC Merced
TEOS- Terrestrial Ecological Observing System
Goals
Evaluation of capabilities and limitations of arrayed systems, integrating sensors, observations, and static measurements:
C, H2O, energy fluxes, and integration with organisms and ecological processes
TEOS: NIMS and Soil Energy Balance
NIMS RD was used at the James Reserve to measure soil surface and sub-surface temperatures. Heat storage varied significantly between seasons, primarily due to water content. Such detailed soil energy balance data for large areas in the understory are unique to NIMS and AMARSS.
scandirection
Imagers as Environmental Sensors
Visible light cameras can capture quantitative information on the behavior of animals: time-to-fledging for cavity nesting birds to reptile diversity.
Visible light cameras can also capture quantitative information in forest understory locations for calculation of Energy Balance parameters. We are just beginning to explore using remote sensing technology for ground based imaging.
Algal growth potential in an urban stream
• Distributed networks of light, temperature, and novel algal growth potential biosensors
• Actuated sampling system followed by lab chemical analyses
• Linking urban runoff (point, non-point source) to water quality
Bioassay Response vs Temp*Light*NO3(Scaled based on Bioassay Respose Curve)
R2 = 0.881
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0 0.05 0.1 0.15 0.2 0.25 0.3Temp (F) * NO3(uM) * Ln(intensity)
Gilbert and Ambrose, UCLA
CENS Prototype EcoPDAGoal is to provide reliable, simple, robust option instead of paper for field crews. In collaboration with TEAM network• Multiple interface options• SQL-lite database on the device• Interactive mapping feature• Flexible export to xml, txt, etc.
Simple MappingInterface
Familiar SpreadsheetInterface
(Web) FormInterface
Outline Sensor Systems (remote + embedded)
What is possible now and in the near future? How do we assess aquatic and terrestrial
ecosystem functions more efficiently? Multi-scale assessment technologies (Integrated
Sensor-Model Systems) How do we evaluate ecosystem function in the
context of human well-being as objectively aspossible? Participatory sensing (enabling the citizen scientist)
Participatory Sensing(e.g., citizenry science using smart phones)
• How many cell phones are there in the world?!
• Image, video, audio, GPS, cell ID, motion band, Bluetooth, text, time, battery level
• Interfaces for many common sensor outputs are there or coming
• Image recognition & classification software
• Make it easy for the user by doing any analysis and visualization on the back-end Web interface
daily trace of an individual
Dietary record
Burke, Estrin et al (UCLA-CENS)
2009 PASIPan-American Sensors for Environmental
Observations (PASEO)
• Sensor fabricators, sensor networkers, ecologists, and environmental scientists
• Sequence of theory and hands-on experiences in:– Building novel sensors– Data transport/communicatiions– Scientific design considerations
• Bahia Blanca, Argentina in April or May 2009• Website: https://eng/ucmerced.edu/paseo/