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
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
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
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
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
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
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
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.
Stacy
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 & 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.
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.
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
Stacy
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.
Clint
Describe the device down selected from technologies including chemiresistive, optical and biological. Choose this based on commercial availability.
Clint
Reduction Reactant + e- = Products Oxidation Reactant = Product + e- electolyte contains free ions that make material electrically conductive
Clint
Clint
Clint
Correlation co efficient ranged from 0.9461 to 0.9923
Clint
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
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.
Paul
Paul
paul
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&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.
Stacy
Stacy
Stacy
Stacy
JC
JC
Delia
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.
delia
Delia
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.
Stacy
Stacy
Stacy
Stacy
Stacy
Stacy
Show Map Series of Blender Test 2
Stacy
Stacy
Stacy
Stacy
Stacy
Stacy
Stacy
Stacy
Stacy
Stacy
Stacy
Stacy
Paul
Paul
Delia
Delia
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.
Delia
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.
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