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Real-time Formaldehyde
Monitoring System
 
IGERT Sensor Science, Engineering
and Informatics (SSEI)
Clint Eaton
J.C. Whittier
Stacy Doore
Delia Massey
Paul Smitherman
• Introduction
• Project Goal and Objectives
• Phase I
– Device Testing
– Network Testing
– System Informatics
• Phase II
– Site Testing
• Commercialization Applications
• Conclusions and Future Work
Formaldehyde Monitoring in Built Environments
O
C
H
H
Formaldehyde Monitoring in Built Environments
Problem:
• Formaldehyde emissions and
toxic exposure concerns,
• Formaldehyde Standards Act (2010) 
• EPA regulations: all wood based
building materials meet new, lower
emissions standards by 2013,
• Can we detect formaldehyde
emission levels in real time and
provide a web-based user interface
for facility managers?
 
Agency/Industry Group Exposure Limit
(TWA-8hr average)
Short-term
Exposure Limit (15
minute maximum)
Threshold
Limit Value
(Ceiling)
NIOSH/CDC (2009) 0.016 ppm (REL) 0.10 ppm 0.10 ppm
ACGIH (2009) ----- ----- 0.30 ppm (TLV)
OSHA (2008) 0.75 ppm (PEL) 2.0 ppm 5.0 ppm
FEMA (2008) 0.016 ppm 0.10 -----
HUD (1985) 0.40 ppm ---- -----
Formaldehyde Monitoring in Built Environments
Effective Date Hardwood
Plywood
Particleboard Medium density
fiberboard
By 1/1/2011 0.05ppm (veneer) 0.09ppm 0.11ppm (MDF)
By 7/1/2012 0.08ppm
(composite)
----- 0.13ppm
(Thin MDF)
U.S. Agency Formaldehyde Exposure Limits
Formaldehyde Standards Act (2010) based on CARB standards
Objectives:
1. Compare the performance of commercially available sensors
and their ability to detect formaldehyde within a dynamic range
of 0.01 and 0.80 ppm.
2. Design and build wireless network architecture to transmit
real-time formaldehyde concentration data.
3. Identify formaldehyde emission patterns in a real world
environment.
4. Develop prototype model for assessing low-level
formaldehyde environmental exposures in real-time.
5. Explore possible changes in existing engineering controls and
exposure assessment processes to improve worker safety.
            
Goal: Design and build wireless sensor network to
detect/monitor formaldehyde emissions in industry setting.
Formaldehyde Monitoring in Built Environments
Formaldehyde Monitoring in Built Environments
Issues raised during alpha test…
• Office question: Were the high readings result of
power flux, lighting, cleaning products, etc.?
• Device Calibration: Could personal exposure badges help?
• Previous EHS testing at AEWC?
• Formaldehyde emissions from human breath?
• Could we use RFID badges to track the location of people?
•Phase I
– Device Testing
– Network Design
– System Informatics
Formaldehyde Monitoring in Built Environments
• Sensor interface – RSR-232 serial with USB adapter
• Sampling method – 10 mL snatch-sample of air taken
by internal pump
• Programmable data collection scheduler
• Supplied calibration standard
• Temperature and humidity corrected
• Response time < 10 sec
• Cost range: $1,100-$3,700
• High sensitivity
• Linear response
• Stable sensitivity
Formaldehyde Monitoring in Built Environments
Formaldemeter htV-M
• Anode: where oxidation occurs,
positive polarity contact
• Cathode: where reduction occurs,
negative polarity contact
• First experiments by Sir William
Grove in 1839
• Electrons generated flow from
anode to cathode
Formaldemeter Electrochemical Sensor
Operation
Formaldehyde Monitoring in Built Environments
Formaldemeter System Block diagram
PRECISION
AMPLIFIER
HIGH RESOLUTION
A-D CONVERTER
MICROPROCESSOR
DISPLAY
EXHAUST
VANEPU
MP
FUEL
CELL
GAS INLET
ELECTRICAL
SIGNAL
• Electrochemical technology
• Snatch sampling via micro pump
• Air drawn into sensor
• Formaldehyde oxidizes to generate
a small current
• Three amplification stages
• High resolution digital sampling
system
Formaldehyde Monitoring in Built Environments
Advantages
•High sensitivity to low
vapor concentrations
•Linear response over wide
conc. range
•Small, rugged and reliable
•Stable sensitivity over long
period of time
•Long working life
Disadvantages
•High cost of production materials
(e.g. precious metals)
•Can be susceptible to
interference effects from certain
other compounds capable of
oxidation
•Different modes of calculating
concentrations
(peak, area, time)
Formaldemeter Summary
Formaldehyde Monitoring in Built Environments
Calibration Method
The Formaldemeter htV-M: 
• calibrated bi-weekly with calibration tool supplied by the
manufacturer
• exposed to formaldehyde using a permeation tube from
Vici at 5 concentrations (.03, .05, .075, .10, .15 ppm)
Formaldehyde Monitoring in Built Environments
Dart HCHO Sensor
• 11 mm two-electrode diffusion sensor
• 250-300 nA/ppm output signal
• Response time is 15 seconds at 20o
C
• Dynamic Range: 0-25 ppm
• Cost: $30-$110
Commercialization Potential
• Circuitry for current to voltage required
• Combine with temperature/humidity
sensors
• Develop concentration curves that are
temperature/humidity dependent
• Algorithm development for marriage of
output voltage to temperature and
humidity data
Formaldehyde Monitoring in Built Environments
ACS Badge:
• Adsorption technology consisting of 
2,4 Dinitrophenylhydrazine
• Lab analyzed with GC-MS
• OSHA gold standard
• provides 8 hour TWA, however...
Scenario 1: .09, .09, .09, .09, .09, .09, .09, .09 = .09  ppm
Scenario 2: .02, .02, .12, .2, .2, .13, .02, .02 = .09 ppm 
Mean ppm exposure statistics obscure the actual risk
associated with shorter term exposure to higher level
formaldehyde emissions.
Formaldehyde Monitoring in Built Environments
Formaldehyde Monitoring in Built Environments
Phase I: Device Calibration, Validation and Selection
Network Design
Network Design/Configuration
• The network consists of 5 wireless sensor node network, a
base station, a Sensor Observation Service (SOS), database
system, and a web-based user interface.
• Each Formaldemeter was connected to an XBee radio.
Readings were output from the serial port to the XBee UART.
• Base station (laptop) collected data from all nodes and pass
it onto the SOS to be stored in a database.
• Web-based user interface displayed latest readings and
could be queried for historical analysis.
Formaldehyde Monitoring in Built Environments
Node Radio Design
PPM RS232
Voltage
11 V peak to peak
Xbee Radio
TTL
Voltage
0-5 V
To Base Station
Voltage
Conversion
Max232a
Voltage
Conversion
Max232a
Sensor nodes
DetectReceive/TransmitProcess/AnalyzeKnowledge/Actio
Base station Web-based
User Interface
ase I: Network Design and Testing
Formaldehyde Monitoring in Built Environments
SOS/SQL Server
Database
Raw Data = Package/StringProcessed Data = Dashboard
Informatics
Use case 1:
Data
Discovery
Unit of
Measurement
Unit of
Measurement
Feature &
Properties
Feature &
Properties
ObservationsObservations
Use case 2:
Sensor
Selection &
Discovery
Sensor typesSensor types
Sensor
capabilities/
restrictions
Sensor
capabilities/
restrictions
Deployment
Systems
Deployment
Systems
Use case 3:
Provenance &
Diagnostics
Use case 4:
Tasking &
Programming
Operating
Restrictions
Operating
Restrictions
Process
model
Process
model
ensor Network Uses Cases and Concepts
Why an Ontology?
Ontology: Provides standardized vocabulary and specification
of concepts and relationships  within or across domains.
Expressed in Web Ontology Language (OWL) which is grounded
in Description Logics (DLs).  Defines concepts, properties
(relationships), and logical combinations of concepts to support
inference.
Advantages:
• Can use existing ontologies, languages, querying, and
reasoning tools
• W3C standards and guidelines in process
• Need system to be able to store and query very large
dynamic datasets
• Semantic modeling of multiple domains allows for creation
of reusable data and interoperability across domains
Formaldehyde Monitoring in Built Environments
Ontology based Linked Data Approach
Domain
ontology
Domain
ontology
Observation
ontology
Observation
ontology
Sensor
Network
ontology
Sensor
Network
ontology
Spatio-
temporal
ontology
Spatio-
temporal
ontology
Exposure
ontology
Exposure
ontology
System &
sensors node
capabilities
Measurement units
Sensor/Person
location
Properties of Entity
Exposure
events
Units
ontology
Units
ontology
hase I: System Informatics
Formaldehyde Monitoring in Built Environments
Database System
• Records observations from
sensors at nodes
• Simplified schema based on
OGC sensor ontologies
• Can store data for PPM,
DART, badge, and location
• Supports changes to the
sensors deployed at a node
and location of the node
Formaldehyde Monitoring in Built Environments
User Interface
Formaldehyde Monitoring in Built Environments
Phase I Accomplishments
• Built wireless sensor network for formaldemeters
• Calibrated the formaldemeters to Vici permeation device
• Investigation into Dart sensor properties
• Conceptual framework guided database development
Formaldehyde Monitoring in Built Environments
Formaldehyde Monitoring in Built Environments
Resin
Blender
• Phase II
– Site Testing
Resin
blender
Resin
Blender
Press
Office
lient Facility: AEWC
Formaldehyde Monitoring in Built Environments
Exploratory Questions for Site
Tests:
1. Under what conditions is it safe to open the blender
door during the resin application process?
2. Where/when are the highest HCHO concentrations
occurring?
3. How do existing HVAC controls impact the HCHO
emissions during typical processes?
4. Are sensors/badges accurately reflecting
concentration measurements?
5. Is there evidence that other work areas are being
impacted by HCHO emissions during manufacturing
processes?
6. Can the system help to identify environmental events
Formaldehyde Monitoring in Built Environments
~8’
~8’
N2
Breathing Zone=
~1ft of nose/mouth
N3
~6’
N4
Side views 1 and 2
N1
N2
N3
N4
N5
Top View
N5N4
Formaldehyde Monitoring in Built Environments
esting Variables:
Sensor Placement
short, long, plume, break)
Resin Type and Volume
Wood Total
Engineering Controls
N1
Test 1,4 and 5
Test 2 and 3
Alpha Test April 20-21
Mean = 0.0244
Median = .0103
Mode = .007
SD = .022
SEM = .0004
Variance = .00
Skew = .89
Range .068
Min = .005
Max = .073
“Dry Run” Test conducted during AEWC client testing.
Formaldehyde resin used with all normal engineering controls in place.
OSHA exceed PEL events (≥ 0.75 ppm)
NIOSH exceed REL events (≥ 0.016 ppm)
OSHA exceed STEL events (≥ 2.0 ppm)
NIOSH > STEL/ceiling events (≥ 0.1 ppm)
Event 1
(4/21 12:32am-8:32am)
Blender Tests April 26
Tests used 5 node wireless system deployed inside/outside blender.
Formaldehyde resin used both with/without normal engineering controls.
Potential Event Thresholds
OSHA exceed PEL events (≥ 0.75 ppm)
NIOSH exceed REL events (≥ 0.016 ppm)
OSHA exceed STEL events (≥ 2.0 ppm)
NIOSH exceed STEL/ceiling events (≥ 0.1 ppm)
Test Hood
Fan
Blender
Fan
Start
Time
Stop
Time
Sensor
Height
(ft)
Fan on
Hood (s)
Time
Door
Open
Resin
Type
1 ON ON 903 907 5 15 910 PUF
2 ON ON 924 927 5 15 930 PUF
3 OFF OFF 951 954 5 0 956 PUF
4 OFF OFF 1044 1047 5 0 1050 PUF
5 OFF OFF 1144
(1147)*
1149 5 0 1151 PUF
Blender Tests (1-5)
Inside Blender
Test 1
Door open
9:10
Test 2
Door open
9:30
Test 3
Door open
9:56
Test 4
Door open
10:50 Test 5
Door open
11:51
Outside Blender
Blender
Test 1
Event
(4/26 9:02am-9:17am)
Test 1
Door open
9:10
Outside Blender (Nodes 2-5)
Inside Blender (Node 1)
Mean = .077
Median = .0688
Mode = .068
SD = .017
SEM = .0027
N = 40
Variance = .000
Skew = .863
Range .049
Min = .058
Max = .107
Descriptives Peak PPM (Nodes 2-5)
Event
(4/26 9:20am-9:35am)
Test 2
Door open
9:30
Blender
Test 2
Outside Blender (Nodes 2-5)
Inside Blender (Node 1)
Mean = .071
Median = .065
Mode = .066
SD = .016
SEM = .002
N = 56
Variance = .000
Skew = 1.00
Range .048
Min = .055
Max = .103
Descriptives Peak PPM (Nodes 2-5)
Event
(4/26 9:56am-10:18am)
Test 3
Door open
9:56
Blender
Test 3
Outside Blender (Nodes 2-5)
Inside Blender (Node 1)
Mean = .088
Median = .084
Mode = .085
SD = .026
SEM = .022
N = 116
Variance = .001
Skew = 1.486
Range .149
Min = .056
Max = .205
Descriptives Peak PPM (Nodes 2-5)
Event
(4/26 10:50am-11:10am)
Test 4
Door open
10:50
Blender
Test 4
Outside Blender (Nodes 2-5)Inside Blender (Node 1)
Mean = .087
Median = .0733
Mode = .073
SD = .038
SEM = .004
N = 72
Variance = .001
Skew = 2.228.
Range .179
Min = .056
Max = .235
Descriptives Peak PPM (Nodes 2-5)
Event
(4/26 11:51am-12:10am)
Test 5
Door open
11:51
Blender
Test 5
Outside Blender (Nodes 2-5)Inside Blender (Node 1)
Mean = .086
Median = .079
Mode = .060
SD = .0311
SEM = .003
N = 88
Variance = .001
Skew = 1.708
Range .130
Min = .060
Max = .190
Descriptives Peak PPM (Nodes 2-5)
Outside Press/Inside Curtain(Nodes2-Inside Press (Node 1)
Board Press
Test 6
Mean = .182
Median = .094
Mode = .060
SD = .350
SEM = .035
N = 96
Variance = .123
Skew = 4.959
Range 2.00
Min = .057
Max = 2.057
Descriptives Peak PPM (Nodes 2-5)
Tues. April 26 Wed. April 27
Board
Emission Test
Mean = .190
Median = .190
Mode = .15
SD = .036
SEM = .0006
N = 2960
Variance = .001
Skew = -0.388
Range .26
Min = .01
Max = .27
Descriptives Peak PPM (Nodes 2-5)
Office Test
Conducted over 8 days to assess ambient air quality in
non-lab areas using only 1 node in data logging mode.
No formaldehyde resin was directly introduced into the
environment at any time.
Event (≥ 2.0 ppm) on 4/26
Events (≥ 0.016 ppm) on 4/21, 4/23, 4/26, 4/27
Events (≥ 0.1 ppm) on 4/23, 4/24, 4/26, 4/27
Mean = 0.018 Mean = 0.018 Mean = 0.016
Mean = 0.03 Mean = 0.094 Mean = 0.013
Mean = 0.188 Mean = 0.163
Office Test (April 20-27)
Office Test MEAN PPM by Day
* sig. at .01 level
*
*
*
*
One way ANOVA
Post Hoc: Tukey HSD
Bonferroni
Office Test HCHO, Temp, Humidity (Zscores)
Office Test HCHO, Temp, Humidity (Zscores)
Pre-Weekend
No Maps?
Insufficient Number of Data Points!
plusσ
• Engineering controls (hood, fan, door) seem to
be working well to protect lab area during
blender process
• Possible emission issues may arise once
boards are pressed and left in lab to dry
• Highest HCHO concentrations occurred during
press processes
• Unexplained HCHO events in office
• System functioned with few node failures
Formaldehyde Monitoring in Built Environments
hase II Exploratory Findings
Next Steps
• Work on new circuit board for DART to design
implement, and test second sensor network
• Concentration verification
• Continue data analysis to identify events
• Collect more data from AEWC offices
• Submit proposals to NSF and EPA for additional R
& D funding
Formaldehyde Monitoring in Built Environments
Unique product to meet identified industry need for
indoor air quality/exposure assessment tools/methods:
• wood product manufacturing
• manufactured homes and RVs
• furniture, carpet, wallboard, paint manufacturing
• mortuary supplies
• hair care products
ommercialization Applications
Formaldehyde Monitoring in Built Environments
So why is this important?
International Center for Toxicology and Medicine 
http://www.ictm.com/Investigation/Root-Cause.aspx
Formaldehyde Monitoring in Built Environments
Conclusions
• Identified immediate need for wireless
formaldehyde monitoring application,
• Tested several commercially available
sensors to deploy in network,
• Designed and implemented wireless network
to collect formaldehyde data in real world
setting, and
• Exploratory analysis and representation of
formaldehyde emissions and exposure
processes.
Formaldehyde Monitoring in Built Environments
Acknowledgements
• NSF IGERT Sensor Science, Engineering and Informatics
DGE Award number 0504494
• Dr. Kate Beard, SSEI Director
• Dr. Brian Frederick, Project Advisor
• Dr. Steven Shaler, Dr. Doug Gardner, Russell Edgar,
and UMaine’s Advanced Structure & Composite Center
Formaldehyde Monitoring in Built Environments
Questions?
Abby NormalAbby Normal
Additional Slides
Calibration Calculations
C(ppm) = (P * (24.46/MW))/Fc)
C = the concentration in PPM by
volume
P = the permeation rate in ng/min
MW = the molecular weight of the
pollutant gas
Fc = the total flow of the calibration
mixture in cc/min
The constant 24.46 is the molar
volume at the reference conditions.
P (ng/min) 29
MW (g/mol) 30
24.46
Fc
(ppm)
Fc
(ppm)
Fc
(ppm)
Fc
(ppm)
Fc
(ppm)
0.03 0.05 0.075 0.1 0.15
23.6 23.6 23.6 23.6 23.6
788.2 472.9 315.3 236.4 157.6
mL/min mL/min mL/min mL/min mL/min
Calibration Calculations
Log P1 = log P0 + a (T1 - T0)
P0 = Rate at temp T0 (°C)
P1 = New rate at temp T1 (°C)
a = 0.030 for high emission tubes
estimate 1°C decrease in
temperature decreases the rate by
10%.
rate in ng/min
P1 29 1.46
P0 60 1.46
T1 19.5
T0 30
Individual Calibrations
Sensitivity and Selectivity of
Formaldemeter
Formaldehyde Sensor Type Electrochemical, two noble
metal electrodes and electrolyte
(proprietary)
Formaldehyde Sensor Dynamic
Range
0.05 -10 ppm
Formaldehyde Sensor
Resolution
0.001 ppm
Formaldehyde Sensor Precision 10% at 2ppm level
Temperature/Humidity Interchangeable digital
CMOSens®
Temperature/Humidity Range -40 to 128 °C, 0-100%
Temperature/Humidity
Accuracy
±0.4°C, ±3% RH
Temperature/Humidity
Calibration
Calibrated to ISO/IEC17025 by
manufacturer
Interference
Compound 1 ppm interference
concentration
Comments
Acetone, Acetic
Acid, Butanol
-- --
Acetaldehyde 8-12 Linear
Ammonia 71000 High Concentration
Carbon Monoxide 100 Linear
Ethylene 160 --
Ethanol, Methanol 12-20, 50 Linear
Phenol, Resorcinol 5,5 Filterable
Permeation Device from Vici
Performance Characteristics of Sensors
Technology Specification Chemisresistive Sensor Optical Sensor Biological Sensor
Sensing Mechanism Metal Oxide Semiconductor Difference Frequency Generator Biological enzymatic reaction
Transduction Process Resistivity change results in
electrical output
MCT Detector Photomultiplier Tube (PMT)
Signal Processing Principal Component Analysis Spectral analysis Algorithms for photon counts
Sensitivity 10’s of ppb (part per billion) 10’s of ppt (parts per trillion) 1’s of ppb
Response/analysis time < 1 minute (ppm) >1 minute
(ppb)
1 minute 2 minutes
Sampling system Micro pump and tubing Multipass absorption cell fed
with ambient air by vacuum
pump
Flow cell comprised of silicone
tube and PMMA cell
Selectivity constraints Poor selectivity Unaffected by humidity Highly selective with minimal
interference
Formaldehyde detection competitors
Sensor
Company
Real
Time
Data
LCD
Display
Wireless
Network
Data
storage/
analysis
Compute
r
Interface
Portable Threshol
d Alarm
OSHA
certified
List
Price
($)
Enmet PPM X X X X X X X 3800
CEA
Instruments
X X X X 2000
Advance
Chemical
Sensors
X X 40
Interscan X X 2000
Environmental
Sensor
Company
X X 1200
Dart Performance Characteristics
Dynamic Range 0.01-25 ppm
Expected Life 5 years in non-corrosive environment
Output signal 250-300 nA/ppm
Temperature Range -10 to 40°C
Pressure Range Up to 10 atmospheres pressure
T90 response time 15 seconds at 20°C
Relative humidity range 15%-90% non-condensing
Typical baseline offset (20°C) 0.02 ppm formaldehyde equivalent
Typical baseline offset (20°C-40°C) 0 to -0.30 ppm (Economy) Premium TBA
Repeatability <+/-2%
Output Linearity Linear
Position Sensitivity None
Storage Life 2 years at 20°C
Need Context for...
• Entity of Interest: Object (Sensor)
• Observation and Measurement
• Entity of Interest: Object (Person)
• Location Context
• Intersection of Person-Location Event and Noteworthy O&M-Location
Event = Exposure Event
o CHEMICAL ENERGY -> ELECTRICAL ENERGY
o Typically consist of two electrodes in contact with an
electrolyte
o ANODE: where oxidation occurs
o CATHODE: where reduction occurs
o Electrons generated flow from anode to cathode
o Similar to galvanic cell (battery): reactions occur
spontaneously
o Reactants are supplied from outside rather than
forming an integral part of its construction
Electrochemical Introduction
Formaldehyde Monitoring in Built Environments

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IGERTSummary

  • 1. Real-time Formaldehyde Monitoring System   IGERT Sensor Science, Engineering and Informatics (SSEI) Clint Eaton J.C. Whittier Stacy Doore Delia Massey Paul Smitherman
  • 2. • Introduction • Project Goal and Objectives • Phase I – Device Testing – Network Testing – System Informatics • Phase II – Site Testing • Commercialization Applications • Conclusions and Future Work Formaldehyde Monitoring in Built Environments O C H H
  • 3. Formaldehyde Monitoring in Built Environments Problem: • Formaldehyde emissions and toxic exposure concerns, • Formaldehyde Standards Act (2010)  • EPA regulations: all wood based building materials meet new, lower emissions standards by 2013, • Can we detect formaldehyde emission levels in real time and provide a web-based user interface for facility managers?
  • 4.   Agency/Industry Group Exposure Limit (TWA-8hr average) Short-term Exposure Limit (15 minute maximum) Threshold Limit Value (Ceiling) NIOSH/CDC (2009) 0.016 ppm (REL) 0.10 ppm 0.10 ppm ACGIH (2009) ----- ----- 0.30 ppm (TLV) OSHA (2008) 0.75 ppm (PEL) 2.0 ppm 5.0 ppm FEMA (2008) 0.016 ppm 0.10 ----- HUD (1985) 0.40 ppm ---- ----- Formaldehyde Monitoring in Built Environments Effective Date Hardwood Plywood Particleboard Medium density fiberboard By 1/1/2011 0.05ppm (veneer) 0.09ppm 0.11ppm (MDF) By 7/1/2012 0.08ppm (composite) ----- 0.13ppm (Thin MDF) U.S. Agency Formaldehyde Exposure Limits Formaldehyde Standards Act (2010) based on CARB standards
  • 5. Objectives: 1. Compare the performance of commercially available sensors and their ability to detect formaldehyde within a dynamic range of 0.01 and 0.80 ppm. 2. Design and build wireless network architecture to transmit real-time formaldehyde concentration data. 3. Identify formaldehyde emission patterns in a real world environment. 4. Develop prototype model for assessing low-level formaldehyde environmental exposures in real-time. 5. Explore possible changes in existing engineering controls and exposure assessment processes to improve worker safety.              Goal: Design and build wireless sensor network to detect/monitor formaldehyde emissions in industry setting. Formaldehyde Monitoring in Built Environments
  • 6. Formaldehyde Monitoring in Built Environments Issues raised during alpha test… • Office question: Were the high readings result of power flux, lighting, cleaning products, etc.? • Device Calibration: Could personal exposure badges help? • Previous EHS testing at AEWC? • Formaldehyde emissions from human breath? • Could we use RFID badges to track the location of people?
  • 7. •Phase I – Device Testing – Network Design – System Informatics Formaldehyde Monitoring in Built Environments
  • 8. • Sensor interface – RSR-232 serial with USB adapter • Sampling method – 10 mL snatch-sample of air taken by internal pump • Programmable data collection scheduler • Supplied calibration standard • Temperature and humidity corrected • Response time < 10 sec • Cost range: $1,100-$3,700 • High sensitivity • Linear response • Stable sensitivity Formaldehyde Monitoring in Built Environments Formaldemeter htV-M
  • 9. • Anode: where oxidation occurs, positive polarity contact • Cathode: where reduction occurs, negative polarity contact • First experiments by Sir William Grove in 1839 • Electrons generated flow from anode to cathode Formaldemeter Electrochemical Sensor Operation Formaldehyde Monitoring in Built Environments
  • 10. Formaldemeter System Block diagram PRECISION AMPLIFIER HIGH RESOLUTION A-D CONVERTER MICROPROCESSOR DISPLAY EXHAUST VANEPU MP FUEL CELL GAS INLET ELECTRICAL SIGNAL • Electrochemical technology • Snatch sampling via micro pump • Air drawn into sensor • Formaldehyde oxidizes to generate a small current • Three amplification stages • High resolution digital sampling system Formaldehyde Monitoring in Built Environments
  • 11. Advantages •High sensitivity to low vapor concentrations •Linear response over wide conc. range •Small, rugged and reliable •Stable sensitivity over long period of time •Long working life Disadvantages •High cost of production materials (e.g. precious metals) •Can be susceptible to interference effects from certain other compounds capable of oxidation •Different modes of calculating concentrations (peak, area, time) Formaldemeter Summary Formaldehyde Monitoring in Built Environments
  • 12. Calibration Method The Formaldemeter htV-M:  • calibrated bi-weekly with calibration tool supplied by the manufacturer • exposed to formaldehyde using a permeation tube from Vici at 5 concentrations (.03, .05, .075, .10, .15 ppm) Formaldehyde Monitoring in Built Environments
  • 13. Dart HCHO Sensor • 11 mm two-electrode diffusion sensor • 250-300 nA/ppm output signal • Response time is 15 seconds at 20o C • Dynamic Range: 0-25 ppm • Cost: $30-$110 Commercialization Potential • Circuitry for current to voltage required • Combine with temperature/humidity sensors • Develop concentration curves that are temperature/humidity dependent • Algorithm development for marriage of output voltage to temperature and humidity data Formaldehyde Monitoring in Built Environments
  • 14. ACS Badge: • Adsorption technology consisting of  2,4 Dinitrophenylhydrazine • Lab analyzed with GC-MS • OSHA gold standard • provides 8 hour TWA, however... Scenario 1: .09, .09, .09, .09, .09, .09, .09, .09 = .09  ppm Scenario 2: .02, .02, .12, .2, .2, .13, .02, .02 = .09 ppm  Mean ppm exposure statistics obscure the actual risk associated with shorter term exposure to higher level formaldehyde emissions. Formaldehyde Monitoring in Built Environments
  • 15. Formaldehyde Monitoring in Built Environments Phase I: Device Calibration, Validation and Selection
  • 17. Network Design/Configuration • The network consists of 5 wireless sensor node network, a base station, a Sensor Observation Service (SOS), database system, and a web-based user interface. • Each Formaldemeter was connected to an XBee radio. Readings were output from the serial port to the XBee UART. • Base station (laptop) collected data from all nodes and pass it onto the SOS to be stored in a database. • Web-based user interface displayed latest readings and could be queried for historical analysis. Formaldehyde Monitoring in Built Environments
  • 18. Node Radio Design PPM RS232 Voltage 11 V peak to peak Xbee Radio TTL Voltage 0-5 V To Base Station Voltage Conversion Max232a Voltage Conversion Max232a
  • 19. Sensor nodes DetectReceive/TransmitProcess/AnalyzeKnowledge/Actio Base station Web-based User Interface ase I: Network Design and Testing Formaldehyde Monitoring in Built Environments SOS/SQL Server Database Raw Data = Package/StringProcessed Data = Dashboard
  • 21. Use case 1: Data Discovery Unit of Measurement Unit of Measurement Feature & Properties Feature & Properties ObservationsObservations Use case 2: Sensor Selection & Discovery Sensor typesSensor types Sensor capabilities/ restrictions Sensor capabilities/ restrictions Deployment Systems Deployment Systems Use case 3: Provenance & Diagnostics Use case 4: Tasking & Programming Operating Restrictions Operating Restrictions Process model Process model ensor Network Uses Cases and Concepts
  • 22. Why an Ontology? Ontology: Provides standardized vocabulary and specification of concepts and relationships  within or across domains. Expressed in Web Ontology Language (OWL) which is grounded in Description Logics (DLs).  Defines concepts, properties (relationships), and logical combinations of concepts to support inference. Advantages: • Can use existing ontologies, languages, querying, and reasoning tools • W3C standards and guidelines in process • Need system to be able to store and query very large dynamic datasets • Semantic modeling of multiple domains allows for creation of reusable data and interoperability across domains Formaldehyde Monitoring in Built Environments
  • 23. Ontology based Linked Data Approach Domain ontology Domain ontology Observation ontology Observation ontology Sensor Network ontology Sensor Network ontology Spatio- temporal ontology Spatio- temporal ontology Exposure ontology Exposure ontology System & sensors node capabilities Measurement units Sensor/Person location Properties of Entity Exposure events Units ontology Units ontology hase I: System Informatics Formaldehyde Monitoring in Built Environments
  • 24. Database System • Records observations from sensors at nodes • Simplified schema based on OGC sensor ontologies • Can store data for PPM, DART, badge, and location • Supports changes to the sensors deployed at a node and location of the node Formaldehyde Monitoring in Built Environments
  • 25. User Interface Formaldehyde Monitoring in Built Environments
  • 26. Phase I Accomplishments • Built wireless sensor network for formaldemeters • Calibrated the formaldemeters to Vici permeation device • Investigation into Dart sensor properties • Conceptual framework guided database development Formaldehyde Monitoring in Built Environments
  • 27. Formaldehyde Monitoring in Built Environments Resin Blender • Phase II – Site Testing Resin blender
  • 29. Exploratory Questions for Site Tests: 1. Under what conditions is it safe to open the blender door during the resin application process? 2. Where/when are the highest HCHO concentrations occurring? 3. How do existing HVAC controls impact the HCHO emissions during typical processes? 4. Are sensors/badges accurately reflecting concentration measurements? 5. Is there evidence that other work areas are being impacted by HCHO emissions during manufacturing processes? 6. Can the system help to identify environmental events Formaldehyde Monitoring in Built Environments
  • 30. ~8’ ~8’ N2 Breathing Zone= ~1ft of nose/mouth N3 ~6’ N4 Side views 1 and 2 N1 N2 N3 N4 N5 Top View N5N4 Formaldehyde Monitoring in Built Environments esting Variables: Sensor Placement short, long, plume, break) Resin Type and Volume Wood Total Engineering Controls N1 Test 1,4 and 5 Test 2 and 3
  • 31. Alpha Test April 20-21 Mean = 0.0244 Median = .0103 Mode = .007 SD = .022 SEM = .0004 Variance = .00 Skew = .89 Range .068 Min = .005 Max = .073 “Dry Run” Test conducted during AEWC client testing. Formaldehyde resin used with all normal engineering controls in place. OSHA exceed PEL events (≥ 0.75 ppm) NIOSH exceed REL events (≥ 0.016 ppm) OSHA exceed STEL events (≥ 2.0 ppm) NIOSH > STEL/ceiling events (≥ 0.1 ppm) Event 1 (4/21 12:32am-8:32am)
  • 32. Blender Tests April 26 Tests used 5 node wireless system deployed inside/outside blender. Formaldehyde resin used both with/without normal engineering controls. Potential Event Thresholds OSHA exceed PEL events (≥ 0.75 ppm) NIOSH exceed REL events (≥ 0.016 ppm) OSHA exceed STEL events (≥ 2.0 ppm) NIOSH exceed STEL/ceiling events (≥ 0.1 ppm) Test Hood Fan Blender Fan Start Time Stop Time Sensor Height (ft) Fan on Hood (s) Time Door Open Resin Type 1 ON ON 903 907 5 15 910 PUF 2 ON ON 924 927 5 15 930 PUF 3 OFF OFF 951 954 5 0 956 PUF 4 OFF OFF 1044 1047 5 0 1050 PUF 5 OFF OFF 1144 (1147)* 1149 5 0 1151 PUF
  • 34. Test 1 Door open 9:10 Test 2 Door open 9:30 Test 3 Door open 9:56 Test 4 Door open 10:50 Test 5 Door open 11:51 Outside Blender
  • 35.
  • 36. Blender Test 1 Event (4/26 9:02am-9:17am) Test 1 Door open 9:10 Outside Blender (Nodes 2-5) Inside Blender (Node 1) Mean = .077 Median = .0688 Mode = .068 SD = .017 SEM = .0027 N = 40 Variance = .000 Skew = .863 Range .049 Min = .058 Max = .107 Descriptives Peak PPM (Nodes 2-5)
  • 37. Event (4/26 9:20am-9:35am) Test 2 Door open 9:30 Blender Test 2 Outside Blender (Nodes 2-5) Inside Blender (Node 1) Mean = .071 Median = .065 Mode = .066 SD = .016 SEM = .002 N = 56 Variance = .000 Skew = 1.00 Range .048 Min = .055 Max = .103 Descriptives Peak PPM (Nodes 2-5)
  • 38. Event (4/26 9:56am-10:18am) Test 3 Door open 9:56 Blender Test 3 Outside Blender (Nodes 2-5) Inside Blender (Node 1) Mean = .088 Median = .084 Mode = .085 SD = .026 SEM = .022 N = 116 Variance = .001 Skew = 1.486 Range .149 Min = .056 Max = .205 Descriptives Peak PPM (Nodes 2-5)
  • 39. Event (4/26 10:50am-11:10am) Test 4 Door open 10:50 Blender Test 4 Outside Blender (Nodes 2-5)Inside Blender (Node 1) Mean = .087 Median = .0733 Mode = .073 SD = .038 SEM = .004 N = 72 Variance = .001 Skew = 2.228. Range .179 Min = .056 Max = .235 Descriptives Peak PPM (Nodes 2-5)
  • 40. Event (4/26 11:51am-12:10am) Test 5 Door open 11:51 Blender Test 5 Outside Blender (Nodes 2-5)Inside Blender (Node 1) Mean = .086 Median = .079 Mode = .060 SD = .0311 SEM = .003 N = 88 Variance = .001 Skew = 1.708 Range .130 Min = .060 Max = .190 Descriptives Peak PPM (Nodes 2-5)
  • 41. Outside Press/Inside Curtain(Nodes2-Inside Press (Node 1) Board Press Test 6 Mean = .182 Median = .094 Mode = .060 SD = .350 SEM = .035 N = 96 Variance = .123 Skew = 4.959 Range 2.00 Min = .057 Max = 2.057 Descriptives Peak PPM (Nodes 2-5)
  • 42. Tues. April 26 Wed. April 27 Board Emission Test Mean = .190 Median = .190 Mode = .15 SD = .036 SEM = .0006 N = 2960 Variance = .001 Skew = -0.388 Range .26 Min = .01 Max = .27 Descriptives Peak PPM (Nodes 2-5)
  • 43. Office Test Conducted over 8 days to assess ambient air quality in non-lab areas using only 1 node in data logging mode. No formaldehyde resin was directly introduced into the environment at any time. Event (≥ 2.0 ppm) on 4/26 Events (≥ 0.016 ppm) on 4/21, 4/23, 4/26, 4/27 Events (≥ 0.1 ppm) on 4/23, 4/24, 4/26, 4/27
  • 44. Mean = 0.018 Mean = 0.018 Mean = 0.016 Mean = 0.03 Mean = 0.094 Mean = 0.013 Mean = 0.188 Mean = 0.163
  • 46. Office Test MEAN PPM by Day * sig. at .01 level * * * * One way ANOVA Post Hoc: Tukey HSD Bonferroni
  • 47. Office Test HCHO, Temp, Humidity (Zscores)
  • 48. Office Test HCHO, Temp, Humidity (Zscores) Pre-Weekend
  • 49. No Maps? Insufficient Number of Data Points!
  • 51. • Engineering controls (hood, fan, door) seem to be working well to protect lab area during blender process • Possible emission issues may arise once boards are pressed and left in lab to dry • Highest HCHO concentrations occurred during press processes • Unexplained HCHO events in office • System functioned with few node failures Formaldehyde Monitoring in Built Environments hase II Exploratory Findings
  • 52. Next Steps • Work on new circuit board for DART to design implement, and test second sensor network • Concentration verification • Continue data analysis to identify events • Collect more data from AEWC offices • Submit proposals to NSF and EPA for additional R & D funding Formaldehyde Monitoring in Built Environments
  • 53. Unique product to meet identified industry need for indoor air quality/exposure assessment tools/methods: • wood product manufacturing • manufactured homes and RVs • furniture, carpet, wallboard, paint manufacturing • mortuary supplies • hair care products ommercialization Applications Formaldehyde Monitoring in Built Environments
  • 54. So why is this important? International Center for Toxicology and Medicine  http://www.ictm.com/Investigation/Root-Cause.aspx Formaldehyde Monitoring in Built Environments
  • 55. Conclusions • Identified immediate need for wireless formaldehyde monitoring application, • Tested several commercially available sensors to deploy in network, • Designed and implemented wireless network to collect formaldehyde data in real world setting, and • Exploratory analysis and representation of formaldehyde emissions and exposure processes. Formaldehyde Monitoring in Built Environments
  • 56. Acknowledgements • NSF IGERT Sensor Science, Engineering and Informatics DGE Award number 0504494 • Dr. Kate Beard, SSEI Director • Dr. Brian Frederick, Project Advisor • Dr. Steven Shaler, Dr. Doug Gardner, Russell Edgar, and UMaine’s Advanced Structure & Composite Center Formaldehyde Monitoring in Built Environments
  • 59. Calibration Calculations C(ppm) = (P * (24.46/MW))/Fc) C = the concentration in PPM by volume P = the permeation rate in ng/min MW = the molecular weight of the pollutant gas Fc = the total flow of the calibration mixture in cc/min The constant 24.46 is the molar volume at the reference conditions. P (ng/min) 29 MW (g/mol) 30 24.46 Fc (ppm) Fc (ppm) Fc (ppm) Fc (ppm) Fc (ppm) 0.03 0.05 0.075 0.1 0.15 23.6 23.6 23.6 23.6 23.6 788.2 472.9 315.3 236.4 157.6 mL/min mL/min mL/min mL/min mL/min
  • 60. Calibration Calculations Log P1 = log P0 + a (T1 - T0) P0 = Rate at temp T0 (°C) P1 = New rate at temp T1 (°C) a = 0.030 for high emission tubes estimate 1°C decrease in temperature decreases the rate by 10%. rate in ng/min P1 29 1.46 P0 60 1.46 T1 19.5 T0 30
  • 62. Sensitivity and Selectivity of Formaldemeter Formaldehyde Sensor Type Electrochemical, two noble metal electrodes and electrolyte (proprietary) Formaldehyde Sensor Dynamic Range 0.05 -10 ppm Formaldehyde Sensor Resolution 0.001 ppm Formaldehyde Sensor Precision 10% at 2ppm level Temperature/Humidity Interchangeable digital CMOSens® Temperature/Humidity Range -40 to 128 °C, 0-100% Temperature/Humidity Accuracy ±0.4°C, ±3% RH Temperature/Humidity Calibration Calibrated to ISO/IEC17025 by manufacturer
  • 63. Interference Compound 1 ppm interference concentration Comments Acetone, Acetic Acid, Butanol -- -- Acetaldehyde 8-12 Linear Ammonia 71000 High Concentration Carbon Monoxide 100 Linear Ethylene 160 -- Ethanol, Methanol 12-20, 50 Linear Phenol, Resorcinol 5,5 Filterable
  • 65. Performance Characteristics of Sensors Technology Specification Chemisresistive Sensor Optical Sensor Biological Sensor Sensing Mechanism Metal Oxide Semiconductor Difference Frequency Generator Biological enzymatic reaction Transduction Process Resistivity change results in electrical output MCT Detector Photomultiplier Tube (PMT) Signal Processing Principal Component Analysis Spectral analysis Algorithms for photon counts Sensitivity 10’s of ppb (part per billion) 10’s of ppt (parts per trillion) 1’s of ppb Response/analysis time < 1 minute (ppm) >1 minute (ppb) 1 minute 2 minutes Sampling system Micro pump and tubing Multipass absorption cell fed with ambient air by vacuum pump Flow cell comprised of silicone tube and PMMA cell Selectivity constraints Poor selectivity Unaffected by humidity Highly selective with minimal interference
  • 66. Formaldehyde detection competitors Sensor Company Real Time Data LCD Display Wireless Network Data storage/ analysis Compute r Interface Portable Threshol d Alarm OSHA certified List Price ($) Enmet PPM X X X X X X X 3800 CEA Instruments X X X X 2000 Advance Chemical Sensors X X 40 Interscan X X 2000 Environmental Sensor Company X X 1200
  • 67. Dart Performance Characteristics Dynamic Range 0.01-25 ppm Expected Life 5 years in non-corrosive environment Output signal 250-300 nA/ppm Temperature Range -10 to 40°C Pressure Range Up to 10 atmospheres pressure T90 response time 15 seconds at 20°C Relative humidity range 15%-90% non-condensing Typical baseline offset (20°C) 0.02 ppm formaldehyde equivalent Typical baseline offset (20°C-40°C) 0 to -0.30 ppm (Economy) Premium TBA Repeatability <+/-2% Output Linearity Linear Position Sensitivity None Storage Life 2 years at 20°C
  • 68. Need Context for... • Entity of Interest: Object (Sensor) • Observation and Measurement • Entity of Interest: Object (Person) • Location Context • Intersection of Person-Location Event and Noteworthy O&M-Location Event = Exposure Event
  • 69.
  • 70. o CHEMICAL ENERGY -> ELECTRICAL ENERGY o Typically consist of two electrodes in contact with an electrolyte o ANODE: where oxidation occurs o CATHODE: where reduction occurs o Electrons generated flow from anode to cathode o Similar to galvanic cell (battery): reactions occur spontaneously o Reactants are supplied from outside rather than forming an integral part of its construction Electrochemical Introduction Formaldehyde Monitoring in Built Environments

Notas do Editor

  1. Hello, My name is Stacy Doore and I am an IGERT Trainee representing the University of Maine’s Sensor Science, Engineering and Informatics Program. Today I would like to very briefly tell you about the work my cohort and I have been doing as a part of our Spring Testbed project involving the development of a wireless formaldehyde monitoring network for industrial built environments.
  2. Stacy
  3. Stacy First, a little background into why we chose this topic for our project. Formaldehyde emissions in indoor air have long been a concern of public health researchers and in some cases has come to the national attention such as the health risks identified by the CDC study on the FEMA trailers deployed after Hurricane Katrina. Based on this and a number of other studies of formaldehyde emissions in indoor environments the Formaldehyde Standards Act was unanimously passed by congress in 2010. Under these new regulations, the EPA will be responsible for ensuring by July 2013 that all wood based building materials such as softwood veneer, plywood, and reconstituted wood products are in compliance with new, lower emissions standards first established by the California Air Resources Board or the CARB standards. These new standards impact many manufacturing businesses in Maine. UMaine has a wood composite research and testing facility on campus, the Advanced Structure &amp; Composite Center that has been listening to industry concerns about regulatory changes Faculty working with these industries brought these concerns to our attention as a potential IGERT testbed project.
  4. Stacy After spending a semester researching the problem from several different domain perspectives and running some preliminary tests, Nasal and eye irritation, neurological effects, and increased risk of asthma and/or allergy at 0.01 to 0.5 ppm.  Eczema and changes in lung function at 0.6 to 1.9 ppm. Cannot be reliably measured in blood, urine, or body tissues following exposure. 
  5. Stacy we defined the testbed project goal and objectives. GOAL The goal of this research is to design and test a real-time formaldehyde monitoring system using wireless sensor network technology to provide an immediate decision support system for users. Objectives: Compare the performance of commercially available sensors and their ability to detect formaldehyde within a dynamic range of 0.01 and 0.80 ppm. Design and build wireless network architecture to transmit real-time formaldehyde emission data. Identify formaldehyde emission patterns in real world environment. Develop prototype model for assessing low-level formaldehyde environmental exposures in real-time. Explore possible changes in existing engineering controls and exposure assessment processes to improve worker safety. * detection range meets CDC NIOSH, FEMA, OSHA, USGBA and ACGIH standards
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  7. Clint Phase I consisted of Prototype Development which involved Device selection, calibration and validation testing, Network development and testing, as well as the creation of data structures, analysis and visualization tools for the system based on identified user needs.
  8. Clint Describe the device down selected from technologies including chemiresistive, optical and biological. Choose this based on commercial availability.
  9. Clint Reduction Reactant + e- = Products Oxidation Reactant = Product + e- electolyte contains free ions that make material electrically conductive
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  12. Clint Correlation co efficient ranged from 0.9461 to 0.9923
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  14. Clint Scenario 1 is below NIOSH REL throughout entire 8 hour minute sampling Scenario 2 is mixed levels with hazardous levels through portions of sampling
  15. Clint Phase One Device testing involved calibrating and validating three commercially available sensors each with a different structure, capabilities and constraints. Sensor 1: was a prepackaged unit capable of collecting formaldehyde concentrations, temperature and humidity. It performed well in the calibration and validation tests but was very expensive, had a slow sampling rate of about a minute, was difficult to convert into a wireless device and used a “black box” approach to its sensor algorithms so it was difficult to see what was going on “under the hood” in terms of signal and response. Sensor 2 was a low cost raw sensor that had potentially a much larger dynamic range. We had to make custom circuit board to be able to convert its signal to voltage and ran into a number of problems during its calibration testing such as an unstable signal and a quick saturation response. Sensor 3 was a an OSHA compliant badge type formaldehyde diffusion sensor used to measure exposures over an 8 hour shift. The badges are then sent into a lab which certifies that the TWA or Time Weighted Average over that 8 hours was at a certain concentration level. The problem with these sensors is the lack of immediate feedback it took over a week to get back the results and the fact that acute exposures could have happened but might have been hidden within the mean.
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  19. Paul So based on our device evaluation, we selected Sensor 1 to develop into the first wireless sensor network. After some trial and error and more circuit board development, the network consisted of six sensors which needed to be modified to be able to pull/send packages of data to an Xbee wireless radio. The radio sent the package to a base station which displayed the raw package data. Informatics of the system concentrated on making raw data useful for creating basic knowledge and decision support tools. The sensor nodes’ packages were sent from the base station to the Sensor Observation Service, an ontology created by 52degreesNorth based on O&amp;M and Sensor ML ontologies designed to handle sensor network data streams. MS SQL server parsed and processed the string into sensor nodes readings in parts per million, temperature, and humidity units for the user. In addition, several user interfaces were created such as the dashboard you see here.
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  27. Delia Phase 2 moved the prototype system into the AEWC to the main testing floor and the large resin blender you see in the picture, as well as an adjacent office. We are actually in the middle of all of this testing as we speak so we don’t have full results to report as of yet but should by the end of this semester.
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  30. Delia We have been trying a number of different formaldehyde based resins, concentrations and engineering control scenarios to measure differences in emissions in each scenario.
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  37. Show Map Series of Blender Test 2 Stacy
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  53. delia We see commercialization potential with the development and refinement of this system that could be broadly applied to not only the wood products manufacturing industry, but also the manufactured and mobile home industry as well as other service based industries using formaldehyde based products such as mortuary services and hair care services.
  54. Delia
  55. delia So in conclusion, we have been able to show some promising preliminary results for our prototype wireless formaldehyde monitoring system during Phase I and should be able to report results for the Phase II portion of our site testing. This project has Identified immediate need for wireless formaldehyde monitoring application, Tested several commercially available sensors to deploy in a wireless network, Designed and implemented wireless network to collect formaldehyde data in real world setting, Created prototype of conceptual model and informatics tools to represent formaldehyde emission and exposure data collection, organization and integration, Our Next Steps will be to continue working to amplify signal of low cost raw sensor for next phase of network development and submit proposals for additional funding.
  56. delia I would like to thank NSF for the support of our IGERT program at the University of Maine, Dr. Kate Beard, our project director and Dr. Brian Frederick, Dr. Steven Shaler our project advisors, and, the SSEI IGERT Cohort 5 who have mentored us through this last year
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