particle emissions from the construction-related grinding ...€¦ · 9:36 12:00 14:24 16:48 time 9...

1
Relative Area -400 -200 0 200 400 m/ z Steel Bolt 1 (from construction site) Steel Bolt 2 Steel Bolt 3 Solid Cu Stainless steel type 304 Stainless steel w/ oil Particle Emissions from the Construction-Related Grinding of Metal and Carpet Glue Samantha Thompson (1), Ross Hamilton (1), Sicelo Masango (1), Mark Zach (2), Deborah Gross (1) 1) Department of Chemistr y , Carleton College, Northfield, MN 55057 2) Department of Physics, Carleton College, Northfield, MN 55057 INTRODUCTION METHODS CONCLUSIONS RESULTS 100 80 60 40 20 0 Number of Particles 11:00 11:30 12:00 12:30 1:00 1:30 2:00 2:30 3:00 3:30 4:00 Time 400 200 0 -200 -400 m/z 200 150 100 50 0 Intensity 2 6 1 0.1 2 6 10 Aerodynamic Diameter (nm) 6 5 4 3 2 1 0 Number of Particles To investigate the composition of the particles emitted, wwe clustered the ATOFMS spectraby similarity, using the K-means algorithm in Enchilada. We found that the data was well represented by 5 clusters, as illustrated in Figure 3, which shows the averages of each of these clusters. The insets how their temporal trends. Note that clusters 1 ,2 and 3 correlate very well with the overall trend for that day, suggesting that they are due to grinding. The fourth and fifth clusters did not contain many particles and do not corelate as well, meaning that they are either background aerosol or are sufficiently small that they don’t settle out as quickly. Their size distributions suggest that size may explain cluster 5, but not cluster 4. In order to investigate the particles emitted by grinding in a more controlled system, we measured when a variety of samples were ground with a similar grinding wheel, in a machine shop. One bolt ground (#1) was removed from the construction site, and is therefore an exact match. Figure 4 shows the average spectra of each sample that was ground. This was done by averaging the particles sampled during the time intervals that the specifieed bolts were ground. Figure 5 shows size concentration data as a function of time from the DRX, APS, and SMPS. The trial with lubricating oil showed particles in a wide size range as compared to the same bolt ground with no lubricating oil. The par- ticles in the lubricating oil trial also stayed suspended for a longer time. In addition to bolt grinding at the construction site, grinding was used to remove old carpet glue from the concrete floor. Sampling of thse particles was carried out in the same way as the metal grinding particles. Figure 6 shows size data from three instruments: the DRX, SMPS, and the APS. They not only show a good corelation but in times of higher total concentration the larger particles ( size range from 4 to 6 μm) increases as well. Figure 7 shows the average mass spectrum of the particles sampled during the glue grinding episodes. Clustering was performed on the particles, with the majority of the particles being placed into one cluster or several mimilar clusters, so it can be assumed that athe majority of the particles are identical. For this reason, an average spectrum is shown here instead of cluster centers. Note the prominent peaks due to high mass polymeric ions, presumably fragments of the glue itself, which is visible in these particles. Acknowledgements: We thank Markus Gälli of TSI, Inc., for the loan of an APS, DusTrak DRX, PPC, and CPC. Funding for this project was provided by Carleton College and the Howard Hughes Medical Institute. Construction was Grinding is a common industrial process in construction-related work. The emissions from grinding metal and other materials can potentially impact the air quality in the region of the work, and thus the health of people who perform the grinding or those nearby. In this study, we measured the size and composition of particles emitted from the grinding of steel bolts and carpet glue in a construction site, as well as the controlled grinding of various metal samples in a machine shop. The steel bolts that were ground contained 95% Fe, with some C, Mn, Cr, V, and W. The bolts and the glue were ground with a grinder containing aluminum oxide, iron oxide, silicon oxide, cryolite, fiberglass, and silicon carbide. Solid samples of copper and stainless steel (type 309) were used in the machine shop. The glue was a standard carpet glue. Various instruments were used, as shown below: Figure 1 shows normalized size distributions of particles sampled with the ATOFMS for each day that metal grinding was sampled. Included in the graph is the data from 6/30/2009, a day on which nothing was done, and which is used as a control. Most of the particles on grinding days are larger than those detected on the control day. Figure 2 shows size, mass spectra and total particle count data from the ATOFMS as a function of time on one grinding day. You can see that during times of increased total particle concentration (bottom panel), the concentration of larger particles increases (top panel). The middle panel shows the temporal evolution of the mass spectrum The five instruments were sampling at 29 meters from the site of emission, a lecture hall at Carleton College. Metal bolts were ground to remove approximately 250 chairs and carpet glue was ground off of concrete, as part of a room renovation. Instrument ATOFMS (TSI 3800) DustTrak DRX (TSI 8534) PPC (TSI 9350) APS (TSI 3321) SMPS (TSI 3936L25) Measured Single-particle composition Mass Concentration Number Concentration Number Concentration Number Concentration Size Range D a = 150 - 3000 nm PM1, PM2.5, PMResp, PM10 D p = 100 - 7000 nm D a = 320 - 20000 nm D m = 15 - 661 nm 0 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 1.00E-01 1.00E+00 1.00E+01 6/29/09 6/30/09 7/13/09 7/14/09 7/15/09 Aerodynamic Diameter t n e c r e P Figure 1 Figure 4 Figure 2 9:36 12:00 14:24 16:48 Time 9:36 12:00 14:24 16:48 Time 9:36 12:00 14:24 16:48 Time 9:36 12:00 14:24 16:48 Time 9:36 12:00 14:24 16:48 Time Cluster 1 1512 Particles Cluster 2 5070 Particles Cluster 3 3528 Particles Cluster 4 1190 Particles Cluster 5 439 Particles Figure 3 309 Steel w/ oil 304 Steel Solid Cu Bolt 3 Bolt 2 Bolt 1 6 8 1 2 4 6 8 10 2 400 300 200 100 0 60 50 40 30 20 10 0 Time Elapsed (min) 0.3 0.4 0.5 0.6 1 2 3 10 8 6 4 2 0 ATOFMS APS 2 3 4 5 6 7 100 6 4 2 0 x10 6 SMPS DRX 0 0.2 0.4 0.6 0.8 1 1.2 1.4 1.6 1.8 Concentration Particle Diameter PM1 PM2.5 RESP PM10 TOTAL Figure 5 Controlled Grinding in the Machine Shop Glue Grinding in Construction Metal Grinding in Construction 4 5 6 7 8 250 200 150 100 50 0 x10 3 14 12 10 8 6 4 2 0 12:00 12:30 1:00 1:30 2:00 2:30 3:00 3:30 4:00 Time 0.5 1 1.5 2 2.5 3 Total Concentration (#/cm 3 ) Particle Diameter Concentration (μg/m 3 ) DRX PM1 PM2.5 RESP PM10 TOTAL Figure 6 Relative Intensity m/z m/z Figure 7 From the various experiments shown here, we can see that the instruments tend to agree about times of increased total particle concentration. We can also see as a general trend that during grinding times the concentration of larger particles increases. The addition of the ATOFMS to the experiments gives us valuable information about the composition of the particles emitted in various grinding activities, including: Grinding particles contain strong signals from metals such as Ca, Fe, Na, K and weaker signals frorm Zn and V. They also contain many organic carbon and elemental carbon particles. Addition of machine oil to a sample bolt ground in the machine shop significantly broadens the size distribution and those particles tend to stay in the air longer. Polymers are visible in particles from grinding glue. m/z Relative Intensity CN - CN - CN - CN - CN - CN - SO2 - SO2 - SO2 - SO2 - SO2 - SO3- HNO3- NO2- OH- Na+ K+ Fe+ =14amu Glue Polymers APS/SMPS APS/SMPS Na + Ca + Fe + Fe + Fe + Zn + CN - CN - CN - SO3 - K + SO3 - Na + C12 + C3H2 + C4 - C8 - C3 + C5 + C11 + SO3 - SO3 - O - Na + Na + Na + Na + Na + Na + K + K + K + K + K + K + Fe + Fe + Fe + Fe + Fe + Fe +

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Page 1: Particle Emissions from the Construction-Related Grinding ...€¦ · 9:36 12:00 14:24 16:48 Time 9 :36 12 0 14:24 16:48 Time 9:36 12:00 14:24 16:48 Time Cluster 1 1512 Particles

Rel

ativ

e A

rea

-400 -200 0 200 400m/z

Steel Bolt 1(from construction site)

Steel Bolt 2

Steel Bolt 3

Solid Cu

Stainless steeltype 304

Stainless steel w/ oil

Particle Emissions from the Construction-Related Grinding of Metal and Carpet Glue Samantha Thompson (1), Ross Hamilton (1), Sicelo Masango (1), Mark Zach (2), Deborah Gross (1)

1) Department of Chemistr y , Carleton College, Northfield, MN 55057 2) Department of Physics, Carleton College, Northfield, MN 55057

INTRODUCTION

METHODS

CONCLUSIONS

RESU L TS

1 0 0

8 0

6 0

4 0

2 0

0 N u m

b e r o

f P a r

t i c l e

s

1 1 : 0 0 1 1 : 3 0 1 2 : 0 0 1 2 : 3 0 1 : 0 0 1 : 3 0 2 : 0 0 2 : 3 0 3 : 0 0 3 : 3 0 4 : 0 0 T i m e

4 0 0

2 0 0

0

- 2 0 0

- 4 0 0

m / z

2 0 0

1 5 0

1 0 0

5 0

0

I n t e n s i t y

2

6 1

0.1

2

6 1 0

A e r o

d y n a

m i c D

i a m e t e

r ( n m

)

6

5

4

3

2

1

0

N u m b e r o f P a r t i c l e s

To investigate the composition of the particles emitted, wwe clustered the ATOFMS spectraby similarity, using the K-means algorithm in Enchilada. We found that the data was well represented by 5 clusters, as illustrated in Figure 3, which shows the averages of each of these clusters. The insets how their temporal trends. Note that clusters 1 ,2 and 3 correlate very well with the overall trend for that day, suggesting that they are due to grinding. The fourth and fifth clusters did not contain many particles and do not corelate as well, meaning that they are either background aerosol or are sufficiently small that they don’t settle out as quickly. Their size distributions suggest that size may explain cluster 5, but not cluster 4.

In order to investigate the particles emitted by grinding in a more controlled system, we measured when a variety of samples were ground with a similar grinding wheel, in a machine shop. One bolt ground (#1) was removed from the construction site, and is therefore an exact match. Figure 4 shows the average spectra of each sample that was ground. This was done by averaging the particles sampled during the time intervals that the specifieed bolts were ground.

Figure 5 shows size concentration data as a function of time from the DRX, APS, and SMPS. The trial with lubricating oil showed particles in a wide size range as compared to the same bolt ground with no lubricating oil. The par-ticles in the lubricating oil trial also stayed suspended for a longer time.

In addition to bolt grinding at the construction site, grinding was used to remove old carpet glue from the concrete floor. Sampling of thse particles was carried out in the same way as the metal grinding particles. Figure 6 shows size data from three instruments: the DRX, SMPS, and the APS. They not only show a good corelation but in times of higher total concentration the larger particles ( size range from 4 to 6μm) increases as well.

Figure 7 shows the average mass spectrum of the particles sampled during the glue grinding episodes. Clustering was performed on the particles, with the majority of the particles being placed into one cluster or several mimilar clusters, so it can be assumed that athe majority of the particles are identical. For this reason, an average spectrum is shown here instead of cluster centers. Note the prominent peaks due to high mass polymeric ions, presumably fragments of the glue itself, which is visible in these particles.

Acknowledgements: We thank Markus Gälli of TSI, Inc., for the loan of an APS, DusTrak DRX, PPC, and CPC. Funding for this project was provided by Carleton College and the Howard Hughes Medical Institute. Construction was

Grinding is a common industrial process in construction-related work. The emissions from grinding metal and other materials can potentially impact the air quality in the region of the work, and thus the health of people who perform the grinding or those nearby.In this study, we measured the size and composition of particles emitted from the grinding of steel bolts and carpet glue in a construction site, as well as the controlled grinding of various metal samples in a machine shop.

The steel bolts that were ground contained 95% Fe, with some C, Mn, Cr, V, and W. The bolts and the glue were ground with a grinder containing aluminum oxide, iron oxide, silicon oxide, cryolite, fiberglass, and silicon carbide. Solid samples of copper and stainless steel (type 309) were used in the machine shop. The glue was a standard carpet glue. Various instruments were used, as shown below:

Figure 1 shows normalized size distributions of particles sampled with the ATOFMS for each day that metal grinding was sampled. Included in the graph is the data from 6/30/2009, a day on which nothing was done, and which is used as a control. Most of the particles on grinding days are larger than those detected on the control day.

Figure 2 shows size, mass spectra and total particle count data from the ATOFMS as a function of time on one grinding day. You can see that during times of increased total particle concentration (bottom panel), the concentration of larger particles increases (top panel). The middle panel shows the temporal evolution of the mass spectrum

The five instruments were sampling at 29 meters from the site of emission, a lecture hall at Carleton College. Metal bolts were ground to remove approximately 250 chairs and carpet glue was ground off of concrete, as part of a room renovation.

InstrumentATOFMS (TSI 3800)DustTrak DRX (TSI 8534)PPC (TSI 9350)APS (TSI 3321)SMPS (TSI 3936L25)

MeasuredSingle-particle compositionMass ConcentrationNumber ConcentrationNumber ConcentrationNumber Concentration

Size RangeDa = 150 - 3000 nmPM1, PM2.5, PMResp, PM10Dp = 100 - 7000 nmDa = 320 - 20000 nmDm = 15 - 661 nm

0

0.01

0.02

0.03

0.04

0.05

0.06

0.07

0.08

0.09

1.00E-01 1.00E+00 1.00E+01

6/29/096/30/097/13/097/14/097/15/09

Aerodynamic Diameter

tnecreP

Figure 1

Figure 4

Figure 2

9:36 12:00 14:24 16:48Time

9:36 12:00 14:24 16:48Time

9:36 12:00 14:24 16:48Time

9:36 12:00 14:24 16:48Time

9:36 12:00 14:24 16:48Time

Cluster 11512 Particles

Cluster 25070 Particles

Cluster 33528 Particles

Cluster 41190 Particles

Cluster 5439 Particles

Figure 3

309Steelw/ oil

304Steel

SolidCu

Bolt3

Bolt2

Bolt1

68

1

2

468

10

2

4003002001000

6050403020100Time Elapsed (min)

0.3

0.40.50.6

1

2

3

1086420

ATOFMS

APS

2

3

4567

100

6

4

2

0

x106

S M P S

DRX

0

0.2

0.4

0.6

0.8

1

1.2

1.4

1.6

1.8

Conc

entra

tion

Part

icle

Dia

met

er

PM1PM2.5RESPPM10TOTAL

Figure 5

Controlled Grinding in the Machine Shop Glue Grinding in Construction

Metal Grinding in Construction

4

5678

250200150100500

x10 3

14121086420

12:00 12:30 1:00 1:30 2:00 2:30 3:00 3:30 4:00Time

0.5

1

1.5

2

2.5

3

Tota

l Co

nce

ntr

atio

n(#

/cm

3 )Pa

rtic

leD

iam

eter

Co

nce

ntr

atio

n(µ

g/m

3 )

DRX

PM1PM2.5RESPPM10TOTAL

Figure 6

Rel

ativ

e In

tens

ity

m/z

m/z

Figure 7

From the various experiments shown here, we can see that the instruments tend to agree about times of increased total particle concentration. We can also see as a general trend that during grinding times the concentration of larger particles increases. The addition of the ATOFMS to the experiments gives us valuable information about the composition of the particles emitted in various grinding activities, including:

Grinding particles contain strong signals from metals such as Ca, Fe, Na, K and weaker signals frorm Zn and V. They also contain many organic carbon and elemental carbon particles. Addition of machine oil to a sample bolt ground in the machine shop significantly broadens the size distribution and those particles tend to stay in the air longer. Polymers are visible in particles from grinding glue.

m/z

Rel

ativ

e In

ten

sity

CN-

CN-

CN-

CN-

CN-

CN-

SO2-

SO2-

SO2-

SO2-

SO2-

SO3-HNO3-

NO2-OH-

Na+

K+

Fe+

=14amu

Glue Polymers

APS/SMPS

APS/SMPS

Na+

Ca+

Fe+

Fe+

Fe+

Zn+CN-

CN-

CN-

SO3-

K+

SO3-

Na+

C12+

C3H2+

C4-

C8-

C3+

C5+

C11+

SO3-

SO3-

O-

Na+

Na+

Na+

Na+

Na+

Na+

K+

K+

K+

K+

K+

K+

Fe+

Fe+

Fe+

Fe+

Fe+

Fe+