Alpha energy adsorption in filters and its potential to degrade air monitoring accuracy. David Ryden November 2008

Size: px
Start display at page:

Download "Alpha energy adsorption in filters and its potential to degrade air monitoring accuracy. David Ryden November 2008"

Transcription

1 Alpha energy adsorption in filters and its potential to degrade air monitoring accuracy. David Ryden November 2008

2 Alpha energy absorption in filters 1. Some basic principals 2. Investigation of spectra obtained from calibrated 239 Pu aerosols collection by filters 3. Performance with heavily degraded spectra 4. Information available in published papers and reports

3 Alpha Energy Degradation can occur 1. In the active aerosol particle (diameters > 1 µm) 2. In the filter material 3. In other particulates collected by the filter 4. In the air gap between filter and detector 5. In the window of the detector Only the last two are taken into account when calibrating with a reference source

4 Alpha Particle Stopping Power and Range

5 Stopping Power of Alpha Particles (MeV/cm) in Air versus Energy Alpha Partices: Stopping Power (Mev per cm air) versus Energy (MeV) Stopping Power (MeV per cm air ) Energy (MeV)

6 Range of Alpha Particles (mg/cm 2 ) versus Energy Alpha Partices: Projected Range (g /m2) versus Energy (MeV) Range (g/m2) Energy (MeV)

7 Range of Alpha Particles (cm) in Air versus Energy 10 Alpha Partices: Projected Range in Air (cm) versus Energy (MeV) y = x x R 2 = Range (cm) Energy (MeV)

8 Approximate ranges of alpha particles Alpha Energy (MeV) Material (mg/cm 2 ) Air (mm) Water (µm)

9 Mass concentrations of aerosols (PM10) found in air Typical Urban sites: Median concentration = 0.05 mg/m 3 (typical range 0.01 to 1mg/m 3 ) Waste Isolation Pilot Plant (WIPP): Median concentration = 5mg/m 3 (range 0.3 to 30mg/m 3 )

10 Time to accumulate significant dust loadings If air containing 0.05 mg/m 3 of particulates is drawn at a rate of 40 LPM through a 25 mm filter then in 24 hours the filter will accumulate a layer equal to 12% of the range of a 5.5 MeV alpha

11 The effects of accumulated particulates The impedance to flow increases as particulates accumulate The efficiency of collecting aerosols tends to increase as the particulates accumulate. For this reason the alphas emitted by freshly collected activity may sometimes suffer less energy degradation with a dirty than with a clean filter. However the energy of alphas emitted by activity already collected on the filter will obviously tend to be degraded by the further collection of additional particulates

12 Some differences in Alpha Spectrum Shapes

13 Difference in spectrum shape with location i-cam COMPARE SPECTRA RECORDED IN DIFFERENT LOCATIONS ITOTAL Location: Pit 3 Location: G11 Snaphot _icam Snaphot _icam3801 ITotal in Pit 3 Channel Counts Channel Number ITotal in G11 x7.84 Extrap ThC' Tail Extrap RaC'Tail Extrap ThC' Tail Extrap RaC'Tail Pit 3 RaA/ThC peak: CN 147 RaC' peak: CN 192 ThC' peak: CN 224 G11 RaA/ThC peak: CN 147 RaC' peak: CN 195 ThC' peak: CN 225

14 The next slide shows an example of improving alpha spectrum resolution with increasing accumulation of aerosol

15 An example of improved energy resolution with accumulated aerosol NRPB Radon Chamber. Changes in spectrum shape with accumulation of test aerosol Filter: Millipore SS After 20 hours After 0.5 hours 1000 Channel Counts 100 T1$7 T1$ Channel Number

16 However note that this is radon progeny spectrum. The short half life of RaA and RaC means that most of their alphas are emitted by relatively freshly collected aerosols This large change in resolution should not be taken as typical

17 Filtration Mechanisms

18 Filtration Efficiency Contributing collection mechanisms versus aerosol particle size Face Velocity = 20 cm/s (6 LPM with 25mm diameter filter, 24 LPM with 50 mm diameter filter) Filter Collection Efficiency 100% 90% 80% Filter fibre dia = 2 micron Filter porosity = 0.92 Filter density = gm/cm3 Face Velocity =20 cm/sec 70% 6 LPM (Filter dia =25 mm) Collection efficiency 60% 50% 40% 30% 20% 10% 0% Particle Diameter (microns) 24 LPM (Filter dia =50 mm) Interception: Impaction: Diffusion: Interaction: Gravitation: Electrostatic: Overall Filter Efficiency:

19 Filtration Efficiency Contributing collection mechanisms versus aerosol particle size Face Velocity = 50 cm/s (15 LPM with 25mm diameter filter, 60 LPM with 50 mm diameter filter) Filter Collection Efficiency 100% 90% 80% Filter fibre dia = 2 micron Filter porosity = 0.92 Filter density = gm/cm3 Face Velocity =50 cm/sec 70% 15 LPM (Filter dia =25 mm) Collection efficiency 60% 50% 40% 30% 20% 10% 0% Particle Diameter (microns) 59 LPM (Filter dia =50 mm) Interception: Impaction: Diffusion: Interaction: Gravitation: Electrostatic: Overall Filter Efficiency:

20 Filtration Efficiency Contributing collection mechanisms versus aerosol particle size Face Velocity = 125 cm/s (37 LPM with 25mm diameter filter, 147 LPM with 50 mm diameter filter) Filter Collection Efficiency 100% 90% 80% Filter fibre dia = 2 micron Filter porosity = 0.92 Filter density = gm/cm3 Face Velocity =125 cm/sec 70% 37 LPM (Filter dia =25 mm) Collection efficiency 60% 50% 40% 30% 20% 10% 0% Particle Diameter (microns) 147 LPM (Filter dia =50 mm) Interception: Impaction: Diffusion: Interaction: Gravitation: Electrostatic: Overall Filter Efficiency:

21 Filtration Efficiency at two face velocities Filter Collection Efficiency Face Velocity =20 cm/s Face Velocity =50 cm/s 100% 95% 90% 85% Collection efficiency 80% 75% 70% 65% 60% 55% 50% Particle Diameter (microns)

22 Spectra from calibrated radioactive aerosols collected on two types of filter

23 239 Pu and 137 Cs aerosols Activity Median Aerodynamic Diameters AMAD =0.4µm AMAD = 4 µm

24 Radon ( 222 Rn) progeny AMAD =0.2µm Equilibrium Factor F=0.4 Concentration= 40Bq/m3

25 Filter materials Whatman GF/A (Glass microfibre) Fluoropore FSLW (3µm PTFE filter)

26 Radon progeny (RaA+RaC ) aerosols (AMAD= 0.4 µm) collected by Whatman GF/A and Fluoropore FSLW flters icam IRSN Spectra: radon-222 progeny collected on GF/A (glass -fibre) and FSLW (PTFE) Filters F12 GFA Radon (F=0.4) F13 FSLW Radon (F=0.4) Fractiobn of Counts in Channel

27 Radon progeny (RaA+RaC ) aerosols (AMAD= 0.4 µm) collected by Whatman GF/A and Fluoropore FSLW flters icam IRSN Spectra: radon-222 progeny collected on GF/A (glass fibre) and FSLW (PTFE) Filters F12 GFA Radon (F=0.4) F13 FSLW Radon (F=0.4) Fraction of counts in channel

28 Pu-239 aerosols (AMAD= 0.4 µm) collected by Whatman GF/A and Fluoropore FSLW flters icam: Spectra from Pu-239 Aerosols of AMAD 0.4 collected on GF/A & FSWL filters F1 Sens Pu-239 (0.4um) GFA (ST= 4.7 hrs) F2 Sens Pu-239 (0.4um) FSWL (ST= 2.1 hrs) Fraction of Spectrum in Channel

29 Pu-239 aerosols (AMAD= 0.4 µm) collected by Whatman GF/A and Fluoropore FSLW flters icam: Spectra from Pu-239 Aerosols of AMAD 0.4 collected on GF/A & FSWL filters 0.1 F1 Sens Pu-239 (0.4um) GFA (ST= 4.7 hrs) F2 Sens Pu-239 (0.4um) FSWL (ST= 2.1 hrs) Fraction of Spectrum in Channel

30 Three test runs with 239 Pu aerosols The instrument sampled air containing 239 Pu aerosols at calibrated concentration levels for between 5 and 6 hours. Air sampling then continued for at least a further 16 hours with activity-free air

31 Three test runs with 239 Pu aerosols Run 1 Filter: Whatman GF/A Aerosol: 239 Pu (AMAD=0.4µm) Mean concentration: 10 Bq/m 3 Duration with 239 Pu: 5 hours 20 minutes Total sampling duration: 22 hours Run 2 Filter: Whatman GF/A Aerosol: 239 Pu (AMAD=4µm) Mean concentration: 13 Bq/m 3 Duration with 239 Pu: 6 hours Total sampling duration: 22 hours Run 3 Filter: Fluoropore FSLW Aerosol: 239 Pu (AMAD=0.4µm) Mean concentration: 9 Bq/m 3 Duration with 239 Pu: 5 hours 20 minutes Total sampling duration: 22 hours

32 239 Pu Concentration and Air Sampling Rate vs Time Filter = GF/A Aerosol AMAD = 0.4µm Pu-239 Conncentration (Bq/m3) and Air Sampling Rate (LPM) vs Time ICARE Alpha Conc (Bq/m3) Resp Pu-239 (0.4um) Filter: GFA Sampling rate M2 (LPM) Pu-239 Concentration (Bq/m3) :00 12:00 14:00 16:00 18:00 20:00 22:00 00:00 02:00 04:00 06:00 08:00 10:00 Air Sampling Rate (LPM)

33 239 Pu Concentration and Air Sampling Rate vs Time Filter = GF/A Aerosol AMAD = 4 µm Pu-237 Concentration (Bq/m3) and Air Sampling Rate (LPM) vs Time Pu-239 Concentration (Bq/m3) Resp Pu-239 (4um) Filter: GFA ICARE Alpha Conc (Bq/m3) Sampling rate M2 (LPM) Air Sampling Rate (LPM) :00 09:00 10:00 11:00 12:00 13:00 14:00 15:00 16:00 17:00

34 Pu-239 Concentration (Bq/m3) Pu-239 Concentration (Bq/m3) and Air Sampling Rate (LPM) vs Time Resp Pu-239 (0.4um) Filter: FSWL ICARE Alpha Conc (Bq/m3) Sampling rate M2 (LPM) :00 11:00 12:00 13:00 14:00 15:00 16:00 17:00 Air Samping Rate (LPM)

35 Fall in Air Sampling Rate as 239 Pu aerosol is collected GF/A filter: The impedance to flow increased moderately with time when sampling 0.4 µm AMAD aerosols. Fluoropore filter: The impedance to flow increased significantly with time when sampling 0.4 µm AMAD aerosols. GF/A filter: The change in impedance to flow was insignificant when sampling 4 µm AMAD aerosols.

36 Fall in Air Sampling Rate as 239 Pu aerosol is collected by filter Filter Pu-239 Aerosol AMAD Initial Air Flow Rate Final Air Flow Rate Fall in Air Flow Rate Fall in Air Flow Rate GF/A 0.4 µm 43 LPM 39 LPM 4 LPM 9 % GF/A 4 µm 42 LPM 41 LPM 1 LPM 2 % FSLW 0.4 µm 49 LPM 39 LPM 10 LPM 20 %

37 Alpha Spectra. Run 1 Filter: Aerosol: Whatman GF/A 239 Pu (AMAD=0.4µm) Mean concentration: 10 Bq/m 3 Duration with 239 Pu: 5 hour 20 minutes Total sampling duration: 22 hours

38 GF/A Filter collecting Pu-239 aerosol (AMAD 0.4) 20 minute counts at hourly intervals Linear Scale icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) GFA (ST= 1 hrs) Pu-239 (0.4um) GFA (ST= 2 hrs) Pu-239 (0.4um) GFA (ST= 3 hrs) Pu-239 (0.4um) GFA (ST= 4 hrs) Pu-239 (0.4um) GFA (ST= 5.4 hrs) Pu-239 (0.4um) GFA (ST= 11.8 hrs) Pu-239 (0.4um) GFA (ST= 22.2 hrs) Fraction of counts in channels

39 GF/A Filter collecting Pu-239 aerosol (AMAD 0.4) 20 minute counts at hourly intervals Log Scale icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes 0.1 Pu-239 (0.4um) GFA (ST= 1 hrs) Pu-239 (0.4um) GFA (ST= 2 hrs) Pu-239 (0.4um) GFA (ST= 3 hrs) Pu-239 (0.4um) GFA (ST= 4 hrs) Pu-239 (0.4um) GFA (ST= 5.4 hrs) Pu-239 (0.4um) GFA (ST= 11.8 hrs) Pu-239 (0.4um) GFA (ST= 22.2 hrs) Fraction of counts in channels

40 GF/A Filter collecting Pu-239 aerosol (AMAD 0.4) 20 minute counts after 1 and 5 hours sampling activity Linear Scale 0.07 icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) GFA (ST= 1 hrs) 0.06 Pu-239 (0.4um) GFA (ST= 5.4 hrs) Fraction of counts in channels

41 GF/A Filter collecting Pu-239 aerosol (AMAD 0.4) 20 minute counts after 1 and 5 hours sampling activity Log Scale 0.1 icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) GFA (ST= 1 hrs) Pu-239 (0.4um) GFA (ST= 5.4 hrs) Fraction of counts in channels

42 GF/A Filter collecting Pu-239 aerosol (AMAD 0.4) 20 minute counts At end of activity-sampling period (5h 20m) and at 12 and 22 hours Linear Scale 0.05 icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) GFA (ST= 5.4 hrs) Pu-239 (0.4um) GFA (ST= 11.8 hrs) Pu-239 (0.4um) GFA (ST= 22.2 hrs) Fraction of counts in channels

43 GF/A Filter collecting Pu-239 aerosol (AMAD 0.4) 20 minute counts At end of activity-sampling period (5h 20m) and at 12 and 22 hours Log Scale 0.1 icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) GFA (ST= 5.4 hrs) Pu-239 (0.4um) GFA (ST= 11.8 hrs) Pu-239 (0.4um) GFA (ST= 22.2 hrs) Fraction of counts in channels

44 GF/A Filter collecting Pu-239 aerosol (AMAD 0.4) 20 minute counts at hourly intervals Integrated Spectrum icam: Integrated spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) GFA (ST= 1 hrs) Pu-239 (0.4um) GFA (ST= 2 hrs) Pu-239 (0.4um) GFA (ST= 3 hrs) Pu-239 (0.4um) GFA (ST= 4 hrs) Pu-239 (0.4um) GFA (ST= 5.4 hrs) Pu-239 (0.4um) GFA (ST= 11.8 hrs) Pu-239 (0.4um) GFA (ST= 22.2 hrs) Fraction of counts in channels

45 GF/A Filter collecting Pu-239 aerosol (AMAD 0.4) 20 minute counts after 1 and 5 hours sampling activity Integrated Spectrum icam: Integrated spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) GFA (ST= 1 hrs) Pu-239 (0.4um) GFA (ST= 5.4 hrs) Fraction of counts in channels

46 Alpha Spectra. Run 2 Filter: Aerosol: Whatman GF/A 239 Pu (AMAD=4µm) Mean concentration: 13 Bq/m 3 Duration with 239 Pu: 5 hour 20 minutes Total sampling duration: 22 hours

47 GF/A Filter Spectra from 4µm Pu-239 aerosols 20 minute counts after 1 hour and 6 hours sampling activity LINEAR SCALE 0.07 icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (4um) GFA (ST= 1 hrs) 0.06 Pu-239 (4um) GFA (ST= 5.9 hrs) Fraction of counts in channels

48 GF/A Filter Spectra from 4µm Pu-239 aerosols 20 minute counts after 1 hour and 6 hours sampling activity LOG SCALE 0.1 icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (4um) GFA (ST= 1 hrs) Pu-239 (4um) GFA (ST= 5.9 hrs) Fraction of counts in channels

49 Comparison of Alpha Spectra from 0.4 µm and 4 µm 239 Pu aerosols

50 GF/A Filters Spectra from 0.4 µm and 4µm Pu-239 aerosols 20 minute counts after 1 hour sampling activity LINEAR SCALE 0.07 icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) GFA (ST= 1 hrs) 0.06 Pu-239 (4um) GFA (ST= 1 hrs) Fraction of counts in channels

51 GF/A Filters Spectra from 0.4 µm and 4µm Pu-239 aerosols 20 minute counts after 1 hour sampling activity LOG SCALE icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) GFA (ST= 1 hrs) Pu-239 (4um) GFA (ST= 1 hrs) Fraction of counts in channels

52 Run 3 Filter: Aerosol: Fluoropore FSLW 239 Pu (AMAD=0.4µm) Mean concentration: 9 Bq/m 3 Duration with 239 Pu: 5 hour 20 minutes Total sampling duration: 22 hours

53 Fluoropore FSLW Filter Spectra from 0.4µm Pu-239 aerosols 20 minute counts after 1 hour and 5h 20m sampling activity LINEAR SCALE 0.09 icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes 0.08 Pu-239 (0.4um) FSLW (ST= 1 hrs) 0.07 Pu-239 (0.4um) FSLW (ST= 5.5 hrs) Fraction of counts in channels

54 Fluoropore FSLW Filter Spectra from 0.4µm Pu-239 aerosols 20 minute counts after 1 hour and 5h 20m sampling activity LOG SCALE 0.1 icam: Spectra from calibrated Pu-239 aerosols_lt=20 minutes Pu-239 (0.4um) FSLW (ST= 1 hrs) Pu-239 (0.4um) FSLW (ST= 5.5 hrs) Fraction of counts in channels

55 The following slides show the increase in the proportion of the 239 Pu alpha counts that fall below the Alpha Region into the Beta Region as aerosol accumulates. Threshold of Alpha Region : Channel Number 60 (Alpha Energy = 2.5 MeV)

56 The increase in the proportion of the 239 Pu alpha counts that fall into the Beta Region during aerosol accumulation Proportion of Pu-239 Alpha signal counts falling below the Alpha Threshold (CN =60, Alpha Energy = 2.5 Mev) 9% Pu-239 (0.4um) GFA Pu-239 (0.4um) FSLW Pu-239 (4um) GFA 8% 7% 6% 5% 4% 3% 2% 1% 0% Elapsed Air Sampling Time (hours)

57 In the three test runs the proportion of 239 Pu alpha signal counts falling below the Alpha Region threshold was: greatest for 0.4µm aerosols collected by a Whatman GF/A filter significantly lower for 0.4µm aerosols collected by a Fluoropore FSLW filter the least for 4µm aerosols collected by a Whatman GF/A filter Presumably the proportion would have been lower with 4µm aerosols collected by a Fluoropore filter The collection of 4µm aerosols by GF/A showed no significant increase in impedance during accumulation

58 The results obtained with calibrated 239 Pu aerosols have shown small but significant losses in alpha signal due to alpha energy absorption by the filter material and by aerosols as they accumulate

59 Alpha Spectra heavily degraded by sampling active water droplets Note: In this example the alpha background is mainly due to thoron progeny ThC and ThC. The RaC contribution is very small

60 Alpha Spectrum acquired over 24 hours since last filter change Before arrival of active water drop LINEAR SCALE SR Snapshot Gross i-cam Spectrum Last Reset: 08:23 23/03/04 Snapshot : 08:16 24/03/04 Elapsed Time:23 hours:54 mins RaA/ThC peak: CN 139 RaC' peak: CN 160 ThC' peak: CN 213 K1= 60 K2= 125 K3= 146 K4= 164 Gross Cnts in A1: Channel Counts Cnts in A2: Cnts in A3: Cnts in A4: Cnts Alpha: Gross K K2 K3 K Channel Number

61 Alpha Spectrum acquired in 60minutes 24 hours since last filter change Before arrival of active water drop LINEAR SCALE SR Snapshot i-cam Spectrum Last Reset: 08:23 23/03/04 Snapshot : 08:16 24/03/04 RaA/ThC peak: CN 139 RaC' peak: CN 159 Gross LT Count Time:60 mins Elapsed Time:23 hours:54 mins ThC' peak: CN K1= 60 K2= 125 K3= 146 K4= 164 Channel Counts Gross LT Cnts in A1: 4002 Cnts in A2: 5285 Cnts in A3: 731 Cnts in A4: Cnts Alpha: Gross LT K1 K2 K3 K Channel Number

62 Alpha Spectrum acquired in 60minutes Before arrival of active water drop LOG SCALE 1000 SR Snapshot Gross LT Count Time:60 mins i-cam Spectrum Snapshot : 08:16 24/03/04 Elapsed Time:23 hours:54 mins RaA/ThC peak: CN 139 RaC' peak: CN 159 ThC' peak: CN 213 K1= 60 K2= 125 K3= 146 K4= Channel Counts Channel Number Gross LT K1 K2 K3 K4 Gross LT Cnts in A1: 4002 Cnts in A2: 5285 Cnts in A3: 731 Cnts in A4: Cnts Alpha: 26099

63 Before arrival of active water drop Predicted ThC + ThC spectrum LOG SCALE SR Snapshot i-cam Spectrum Snapshot : 08:16 24/03/04 SpecSSp Tn2CtbSS+Tn1CtbSS Count Time:60 mins Elapsed Time:23 hours:54 mins Channel Counts Gross LT Tn2CtbSS+Tn1CtbSS K1 K2 K3 K4 K1= 60 K2= 125 K3= 146 K4= 164 Gross LT Cnts in A1: 4002 Cnts in A2: 5285 Cnts in A3: 731 Cnts in A4: Cnts Alpha: Tn2CtbSS+Tn1CtbS Cnts in A1: 4003 Cnts in A2: Cnts in A3: Cnts in A4: Cnts Alpha: SpecSSp Cnts in A1: -1 Cnts in A2: Cnts in A3: Cnts in A4: 0 Cnts Alpha: Channel Number

64 Before arrival of active water drop Predicted ThC + ThC spectrum LINEAR SCALE Channel Counts SR Snapshot Gross LT Tn2CtbSS+Tn1CtbSS K1 K2 K3 K4 i-cam Spectrum Count Time:60 mins Snapshot : 08:16 24/03/04 Elapsed Time:23 hours:54 mins K1= 60 K2= 125 K3= 146 K4= 164 Gross LT Cnts in A1: 4002 Cnts in A2: 5285 Cnts in A3: 731 Cnts in A4: Cnts Alpha: Tn2CtbSS+Tn1CtbS Cnts in A1: 4003 Cnts in A2: Cnts in A3: Cnts in A4: Cnts Alpha: SpecSSp Cnts in A1: -1 Cnts in A2: Cnts in A3: Cnts in A4: 0 Cnts Alpha: Channel Number

65 Before arrival of active water drop LINEAR SCALE Spectrum after thoron progeny spectra stripped SR Snapshot i-cam Spectrum Elapsed Time:23 hours:54 mins Channel Counts SpecSSp Tn2CtbSS+Tn1CtbSS SpecSSp K1 K2 K3 K4 Count Time:60 mins K1= 60 K2= 125 K3= 146 K4= 164 Gross LT Cnts in A1: 4002 Cnts in A2: 5285 Cnts in A3: 731 Cnts in A4: Cnts Alpha: Tn2CtbSS+Tn1CtbS Cnts in A1: 4003 Cnts in A2: Cnts in A3: Cnts in A4: Cnts Alpha: SpecSSp Cnts in A1: -1 Cnts in A2: Cnts in A3: Cnts in A4: 0 Cnts Alpha: Channel Number

66 Before arrival of active water drop LINEAR SCALE Residual spectrum after radon and thoron progeny spectra stripped Channel Counts SR Snapshot Comp. LT i-cam Spectrum Count Time:60 mins Last Reset: 08:23 23/03/04 Snapshot : 08:16 24/03/04 Elapsed Time:23 hours:54 mins K1= 60 K2= 125 K3= 146 K4= 164 Gross LT Cnts in A1: 4002 Cnts in A2: 5285 Cnts in A3: 731 Cnts in A4: Cnts Alpha: SpecSSp Cnts in A1: -1 Cnts in A2: Cnts in A3: Cnts in A4: 0 Cnts Alpha: SpecSS2p Cnts in A1: -77 Cnts in A2: Cnts in A3: 0 Cnts in A4: 0 Cnts Alpha: SpecSS3p 0 Cnts in A1: Cnts in A2: 0 Cnts in A3: -0.1 Cnts in A4: Cnts Alpha: Channel Number

67 Before arrival of active water drop LINEAR SCALE Residual spectrum after radon and thoron progeny spectra stripped Channel Counts SR Snapshot Comp. LT i-cam Spectrum Count Time:60 mins Last Reset: 08:23 23/03/04 Snapshot : 08:16 24/03/04 Elapsed Time:23 hours:54 mins K1= 60 K2= 125 K3= 146 K4= 164 Gross LT Cnts in A1: 4002 Cnts in A2: 5285 Cnts in A3: 731 Cnts in A4: Cnts Alpha: SpecSSp Cnts in A1: -1 Cnts in A2: Cnts in A3: Cnts in A4: 0 Cnts Alpha: SpecSS2p Cnts in A1: -77 Cnts in A2: Cnts in A3: 0 Cnts in A4: 0 Cnts Alpha: SpecSS3p -20 Cnts in A1: Cnts in A2: 0 Cnts in A3: -0.1 Cnts in A4: 0-40 Cnts Alpha: Channel Number

68 Before arrival of active water drop LINEAR SCALE SR Snapshot i-cam Spectrum Last Reset: 08:23 23/03/04 Snapshot : 08:16 24/03/04 RaA/ThC peak: CN 139 RaC' peak: CN 159 Gross LT Count Time:60 mins Elapsed Time:23 hours:54 mins ThC' peak: CN K1= 60 K2= 125 K3= 146 K4= 164 Channel Counts Gross LT Cnts in A1: 4002 Cnts in A2: 5285 Cnts in A3: 731 Cnts in A4: Cnts Alpha: Gross LT K1 K2 K3 K Channel Number

69 After arrival of active water drop LINEAR SCALE SR Snapshot i-cam Spectrum Last Reset: 08:23 23/03/04 Snapshot : 13:11 24/03/04 RaA/ThC peak: CN 128 RaC' peak: CN 160 Gross LT Count Time:60 mins Elapsed Time:28 hours:48 mins ThC' peak: CN K1= 60 K2= 125 K3= 146 K4= 164 Channel Counts Gross LT Cnts in A1: 8244 Cnts in A2: 3200 Cnts in A3: 1171 Cnts in A4: Cnts Alpha: Gross LT K1 K2 K3 K Channel Number

70 After arrival of active water drop Predicted ThC + ThC spectrum LINEAR SCALE SR Snapshot SpecSSp Tn2CtbSS+Tn1CtbSS i-cam Spectrum Count Time:60 mins Last Reset: 08:23 23/03/04 Snapshot : 13:11 24/03/04 Elapsed Time:28 hours:48 mins RaA/ThC peak: CN 145 RaC' peak: CN 160 Channel Counts Gross LT Tn2CtbSS+Tn1CtbSS K1 K2 K3 K4 Gross LT RaA/ThC peak: CN 128 RaC' peak: CN 160 ThC' peak: CN 202 K1= 60 K2= 125 K3= 146 K4= 164 Gross LT Cnts in A1: 8244 Cnts in A2: 3200 Cnts in A3: 1171 Cnts in A4: Cnts Alpha: Tn2CtbSS+Tn1CtbS Cnts in A1: 6608 Cnts in A2: 3365 Cnts in A3: Cnts in A4: Cnts Alpha: SpecSSp Cnts in A1: 1636 Cnts in A2: -165 Cnts in A3: Cnts in A4: 0 Cnts Alpha: Channel Number

71 After arrival of active water drop LINEAR SCALE Spectra before and after thoron progeny spectra stripped Channel Counts SR Snapshot SpecSSp Gross LT SpecSSp K1 K2 K3 K4 Tn2CtbSS+Tn1CtbSS i-cam Spectrum Count Time:60 mins Elapsed Time:28 hours:48 mins K1= 60 K2= 125 K3= 146 K4= 164 Gross LT Cnts in A1: 8244 Cnts in A2: 3200 Cnts in A3: 1171 Cnts in A4: Cnts Alpha: Tn2CtbSS+Tn1CtbS Cnts in A1: 6608 Cnts in A2: 3365 Cnts in A3: Cnts in A4: Cnts Alpha: SpecSSp Cnts in A1: 1636 Cnts in A2: Cnts in A3: Cnts in A4: 0 Cnts Alpha: Channel Number

72 After arrival of active water drop LINEAR SCALE Spectrum after thoron progeny spectra stripped Channel Counts SR Snapshot SpecSSp SpecSSp K1 K2 K3 K4 Tn2CtbSS+Tn1CtbSS i-cam Spectrum Count Time:60 mins Elapsed Time:28 hours:48 mins K1= 60 K2= 125 K3= 146 K4= 164 Gross LT Cnts in A1: 8244 Cnts in A2: 3200 Cnts in A3: 1171 Cnts in A4: Cnts Alpha: Tn2CtbSS+Tn1CtbS Cnts in A1: 6608 Cnts in A2: 3365 Cnts in A3: Cnts in A4: Cnts Alpha: SpecSSp Cnts in A1: 1636 Cnts in A2: Cnts in A3: Cnts in A4: 0 Cnts Alpha: Channel Number

73 After arrival of active water drop LINEAR SCALE Residual spectrum after radon and thoron progeny spectra stripped SR Snapshot i-cam Spectrum Count Time:60 mins Snapshot : 13:11 24/03/04 Elapsed Time:28 hours:48 mins K1= 60 K2= 125 K3= 146 K4= Comp. LT Gross LT Cnts in A1: 8244 Cnts in A2: 3200 Cnts in A3: 1171 Cnts in A4: Cnts Alpha: Channel Counts SpecSSp Cnts in A1: 1636 Cnts in A2: -165 Cnts in A3: Cnts in A4: 0 Cnts Alpha: SpecSS2p Cnts in A1: Cnts in A2: Cnts in A3: 0 Cnts in A4: 0 Cnts Alpha: Comp. LT 80 Cnts in A1: Cnts in A2: 0 Cnts in A3: -0.1 Cnts in A4: 0-20 Cnts Alpha: Channel Number

74 After arrival of active water drop LINEAR SCALE Residual spectrum after radon and thoron progeny spectra stripped SR Snapshot Comp. LT i-cam Spectrum Count Time:60 mins Snapshot : 13:11 24/03/04 Elapsed Time:28 hours:48 mins K1= 60 K2= 125 K3= 146 K4= 164 Gross LT Cnts in A1: 8244 Cnts in A2: 3200 Cnts in A3: 1171 Cnts in A4: Cnts Alpha: Channel Counts SpecSSp Cnts in A1: 1636 Cnts in A2: -165 Cnts in A3: Cnts in A4: 0 Cnts Alpha: SpecSS2p Cnts in A1: Cnts in A2: Cnts in A3: 0 Cnts in A4: 0 Cnts Alpha: Comp. LT Cnts in A1: Cnts in A2: 0 Cnts in A3: -0.1 Cnts in A4: 0-20 Cnts Alpha: Channel Number

75 Counting the filter 7 days after removing it from the monitor confirmed the that the long lived alpha activity recorded by icam in real-time was due to 241 Am/ 239 Pu

76 Information from papers and reports The following is a list of some papers and reports that contain useful information

77 Pickering (1984) discusses self absorption as alpha energy in escaping from their individual aerosol particles Pickering and Fourcaudot (1987) describe how alpha-recoil affects the distribution of aerosols in filters Seiler, Newton and Guilmett (1988) give detailed theoretical models for continuous monitoring in a dusty environment

78 Moore, McFarland and Rodgers (1993) describe the factors that affect alpha particle detection by continuous air monitors Huang, Schery, Alcantara and Rodgers (2002) discuss the influence of dust loading on the alpha-particle energy resolution of continuous air monitors Huang, Schery, Alcantara, Dale and Rodgers (2002) provide useful information in a paper on test aerosols

79 Investigation of techniques to improve Continuous Air Monitors under conditions of high dust loading in environmental settings US DoE Report This is a particularly useful report by Huang et al Luetzelschwab, Storey, Zraly and Dussinger (200) describes measurements of self absorption of alpha energy in filters but only with sources rather than active aerosols Grivaud (1992) discusses alpha spectrum resolution obtained with different filters Grivaud and Pagliardini (2001) give a detailed assessment of Fluoropore FSLW (version 2)

80 Tony Geryes is two years into a doctoral thesis (Paris University) entitled Etude de la degradation de l energy des particules Alpha dans les filtres de surveillance de la radioactivity atmospheric He is supervised by Dr Celine Monsanglant Louvet at IRSN. When completed this promises to be a most useful study

ENVIRONMENTAL SAMPLING

ENVIRONMENTAL SAMPLING ENVIRONMENTAL SAMPLING 1. GENERAL. Collecting and analyzing samples provides numerical data that describe a particular situation. The ASHG shall direct sampling procedures. The sampling criteria shall

More information

Integrating Radon Progeny Monitor

Integrating Radon Progeny Monitor Integrating Radon Progeny Monitor Y. Ishimori, K. Ito and S. Furuta Ningyo-toge Environmental Engineering Center, Japan Nuclear Cycle Development Institute, 1550 Kamisaibara, Tomata-gun, Okayama 708-0698

More information

Radon Progeny Size Distribution in and around Closed Uranium Mine

Radon Progeny Size Distribution in and around Closed Uranium Mine Radon Progeny Size Distribution in and around Closed Uranium Mine Kimio ITO, Yuu ISHIMORI, Sada-aki FURUTA JNC Ningyo-toge, 155 Kamisaibara-son Tomata-gun Okayama, 78-698, Japan INTRODUCTION The Japan

More information

Air monitoring around the world.

Air monitoring around the world. Air monitoring around the world. Regulatory considerations and testing solutions for particulate matter in ambient air. EMD Millipore Corp. is a subsidiary of Merck KGaA, Darmstadt, Germany 1 One planet.

More information

Sampling for Airborne Radioactivity

Sampling for Airborne Radioactivity Sampling for Airborne Radioactivity Peter D. Harty Human Protection and Performance Division Defence Science and Technology Organisation DSTO-TN-0782 ABSTRACT This report examines how to sample airborne

More information

Sampling for particulates

Sampling for particulates Sampling for particulates EOH 466B Evaluating the Occupational Environment Spring 2004 Overview Draw known volume of air past filter. Filter is tube, paper, etc. Use size pre-selector according to hazard.

More information

Sampling for particulates

Sampling for particulates Sampling for particulates EOH 466B Evaluating the Occupational Environment Spring 2008 Overview Draw known volume of air past filter. Filter is tube, paper, etc. Use size pre-selector according to hazard.

More information

RESIDENTIAL RADON LEVELS IN HONG KONG

RESIDENTIAL RADON LEVELS IN HONG KONG RESIDENTIAL RADON LEVELS IN HONG KONG Derek R. Lane-Smith NITON Corporation Bedford, MA ABSTRACT Hong Kong is made of concrete, which emits radon continuously. The radon concentration in a domestic apartment

More information

Initial Sand Mine and Processing Plant Particulate Levels. Crispin Pierce PhD University of Wisconsin-Eau Claire 20 January 2013

Initial Sand Mine and Processing Plant Particulate Levels. Crispin Pierce PhD University of Wisconsin-Eau Claire 20 January 2013 Initial Sand Mine and Processing Plant Particulate Levels Crispin Pierce PhD University of Wisconsin-Eau Claire 20 January 2013 Sampling Instruments: DustTrak Aerosol Monitor DustTrak model 8520 aerosol

More information

Annual inhalation dose of indoor radon in dwellings in Aizawl City, Mizoram, India

Annual inhalation dose of indoor radon in dwellings in Aizawl City, Mizoram, India Science Vision www.sciencevision.org Science Vision www.sciencevision.org Science Vision www.sciencevision.org Science Vision www.sciencevision.org Original Research Science Vision 16 (1) January-March

More information

RADON PROGENY IN EGYPTIAN UNDERGROUND PHOSPHATE MINES

RADON PROGENY IN EGYPTIAN UNDERGROUND PHOSPHATE MINES Radiation Protection Dosimetry Vol. 95, No. 1, pp. 63 68 (2001) Nuclear Technology Publishing TECHNICAL NOTE RADON PROGENY IN EGYPTIAN UNDERGROUND PHOSPHATE MINES M. A. El-Hady, A. Mohammed, A. El-Hussein,

More information

Beta Attenuation Mass Monitor

Beta Attenuation Mass Monitor BAM-1020 Beta Attenuation Mass Monitor PM 2.5 FEM Configuration The New Evolution of BAM Technology Dennis Hart Met One Instruments, Inc. Rev C July 2008 4/23/2009 1 Overview The Big Picture The success

More information

THE LEADER IN PERFORMANCE INDOOR AIR QUALITY MEASUREMENTS

THE LEADER IN PERFORMANCE INDOOR AIR QUALITY MEASUREMENTS THE LEADER IN PERFORMANCE INDOOR AIR QUALITY MEASUREMENTS INDOOR AIR QUALITY INSTRUMENTS UNDERSTANDING, ACCELERATED BREATHE A LITTLE EASIER WITH TSI Indoor air quality is a growing concern. With the increasing

More information

What is a positron moderator?

What is a positron moderator? What is a positron moderator? The advent of slow positron beams has resulted in nondestructive depth profiling of defects in surfaces and interfaces, low energy positron diffraction and positron remission

More information

Radioisotope Batteries. Jake Blanchard University of Wisconsin April 2010

Radioisotope Batteries. Jake Blanchard University of Wisconsin April 2010 Radioisotope Batteries Jake Blanchard University of Wisconsin April 2010 Introduction Radioisotope batteries provide reliable batteries with high energy density They are valuable when long life is needed

More information

Modeling the Inhalation Exposure Pathway in Performance Assessment of Geologic Radioactive Waste Repository at Yucca Mountain

Modeling the Inhalation Exposure Pathway in Performance Assessment of Geologic Radioactive Waste Repository at Yucca Mountain Modeling the Inhalation Exposure Pathway in Performance Assessment of Geologic Radioactive Waste Repository at Yucca Mountain M.A. Wasiolek Sandia National Laboratories 1180 N. Town Center Dr., Las Vegas,

More information

INVESTIGATION OF RADON, THORON, AND THEIR PROGENY NEAR THE EARTH'S SURFACE. ID 29D-9HF010) 1 January 1994 through 31 December 1997

INVESTIGATION OF RADON, THORON, AND THEIR PROGENY NEAR THE EARTH'S SURFACE. ID 29D-9HF010) 1 January 1994 through 31 December 1997 doerep.98a FINAL REPORT INVESTIGATION OF RADON, THORON, AND THEIR PROGENY NEAR THE EARTH'S SURFACE DOE GRANT DE-FGO3-94ER61781(J!JMIMT ID 29D-9HF010) 1 January 1994 through 31 December 1997 S. D. Schery

More information

Line filters LINE FILTERS

Line filters LINE FILTERS Line filters LINE FILTERS 45-2430 Worthington Creyssensac s heritage Creyssensac was founded in Nanterre (near Paris), France in 934 by Elie Creyssensac and quickly became renowned in the automotive industry

More information

Air Quality Measurement Methods. Tim Morphy Regional Manager Thermo Electron October 20 th, 2006

Air Quality Measurement Methods. Tim Morphy Regional Manager Thermo Electron October 20 th, 2006 Air Quality Measurement Methods Tim Morphy Regional Manager Thermo Electron October 20 th, 2006 Main Criteria Pollutants US EPA Federal Reference Methods US EPA Federal Equivalent Methods http://www.epa.gov/ttn/amtic/criteria.html

More information

WATER & PARTICULATE CONTAMINATION IN OIL & LUBRICATED SYSTEMS

WATER & PARTICULATE CONTAMINATION IN OIL & LUBRICATED SYSTEMS IN OIL & LUBRICATED SYSTEMS Author: Tony Arenas, Y2K Fluid Power, Tony.Arenas@y2kfluidpower.com Abstract or Executive Summary Every major sustainable market in the world from Power Generation, AG, and

More information

Research Report. Determination of Formaldehyde Using The SKC UMEx 100 (Cat. No ) Diffusive Sampler. Abstract

Research Report. Determination of Formaldehyde Using The SKC UMEx 100 (Cat. No ) Diffusive Sampler. Abstract Research Report Determination of Formaldehyde Using The SKC UMEx 100 (Cat. No. 500-100) Diffusive Sampler Abstract A sampling method for formaldehyde in air using a UMEx 100 Diffusive Sampler has been

More information

F-Series 1 Elements Performance Validation

F-Series 1 Elements Performance Validation F-Series 1 Elements Performance Validation An independent test report validating the performance of the nano F-Series 1 Compressed Air & Gas Filter Elements to ISO 12500-1:2007 air quality standards. Conducted

More information

Chemical composition and source apportionment of PM 1.0, PM 2.5 and PM in the roadside environment of Hong Kong

Chemical composition and source apportionment of PM 1.0, PM 2.5 and PM in the roadside environment of Hong Kong Chemical composition and source apportionment of PM 1.0, PM 2.5 and PM 10-2.5 in the roadside environment of Hong Kong Dr. Cheng Yan Department of Environmental Science and Technology School of Human Settlements

More information

Line Filters Solid, simple, smart. Advanced reliability in compressed air. TECHNOLOGY YOU CAN TRUST

Line Filters Solid, simple, smart. Advanced reliability in compressed air. TECHNOLOGY YOU CAN TRUST Line Filters 7-0 Solid, simple, smart. Advanced reliability in compressed air. AVAILABILITY PARTNERSHIP SERVICEABILITY TECHNOLOGY YOU CAN TRUST RELIABILITY SIMPLICITY AVAILABILITY PARTNERSHIP SERVICEABILITY

More information

EVERGREEN: IMPROVING THE LIFETIME OF PLASTIC SCINTILLATORS

EVERGREEN: IMPROVING THE LIFETIME OF PLASTIC SCINTILLATORS EVERGREEN: IMPROVING THE LIFETIME OF PLASTIC SCINTILLATORS Mike Kusner and Peter Menge Saint-Gobain Crystals, Hiram Ohio USA BACKGROUND: Thousands of plastic scintillators are deployed outdoors where they

More information

Radiation

Radiation Radiation 04 Background radiation occurs all around us and is easily measured and controlled. In fact, the radiation risks to those working and living near a mine are very low. June 2016 WWW.ARULTD.COM

More information

Sample Conditioning Instruments. Jonna Kannosto Technical Marketing Specialist, PhD

Sample Conditioning Instruments. Jonna Kannosto Technical Marketing Specialist, PhD Sample Conditioning Instruments Jonna Kannosto Technical Marketing Specialist, PhD Dekati Solutions: Complete setups It s not only the source or measurement instrument! It s also how to take a proper sample!

More information

PREFILTERS/DEPTH TYPE M EDIA

PREFILTERS/DEPTH TYPE M EDIA PREFILTERS/DEPTH TYPE M EDIA Prefilters/Depth Type Media Cellulose Fiber Filters Glass Fiber Filters Quartz Fiber Filters Specifications: Glass/Quartz Fiber Polyflon PTFE Fiber Filters Dacron Mesh Separators

More information

REAL-TIME DUST MONITOR TEOM 1405-F

REAL-TIME DUST MONITOR TEOM 1405-F PRODUCT DATASHEET - The TEOM 1405 Real-time Dust Monitor measures airborne dust, volatile and semi-volatile compounds in real time. It the immediate replacement of the FDMS module equipped TEOM 1400 analyser,

More information

WM2012 Conference, February 26 - March 1, 2012, Phoenix, AZ USA

WM2012 Conference, February 26 - March 1, 2012, Phoenix, AZ USA Considerations for Implementation of MARSSIM/MARSAME Surface Radioactivity Surveys within FUSRAP - 12330 Scott S. Hay*, Michael S. Winters*, *Cabrera Services, Inc., East Hartford, Connecticut ABSTRACT

More information

ANALYSIS OF PARTICULATE POLLUTANT (PM 2.5 ) AND GASEOUS POLLUTANT (CO) AT JABALPUR, MP

ANALYSIS OF PARTICULATE POLLUTANT (PM 2.5 ) AND GASEOUS POLLUTANT (CO) AT JABALPUR, MP International Journal of Science, Environment and Technology, Vol. 4, No 5, 2015, 1344 1350 ISSN 2278-3687 (O) 2277-663X (P) ANALYSIS OF PARTICULATE POLLUTANT (PM 2.5 ) AND GASEOUS POLLUTANT (CO) AT JABALPUR,

More information

WBEA Standard Operating Procedure

WBEA Standard Operating Procedure Page 1 WBEA Standard Operating Procedure SOP Title Procedures for operating continuous R&P TEOM PM 10 and PM 2.5 Analyzers Author Implementation date February 1 st 2013 Revision History Revision # Date

More information

This document is a preview generated by EVS

This document is a preview generated by EVS INTERNATIONAL STANDARD ISO 16890-1 First edition 2016-12-01 Air filters for general ventilation Part 1: Technical specifications, requirements and classification system based upon particulate matter efficiency

More information

PROCEEDINGS. Introduction. Olga Stawarz, Maria Karpińska, Kalina Mamont-Ciesla

PROCEEDINGS. Introduction. Olga Stawarz, Maria Karpińska, Kalina Mamont-Ciesla NUKLEONIKA 2006;51(Supplement 2):S53 S57 PROCEEDINGS Investigation of the influence of high humidity and exposure duration on the measurement results of radon concentration by means of PicoRad system in

More information

S2 RANGER LE: Analysis of Light Elements in Cement, Slags and Feldspar

S2 RANGER LE: Analysis of Light Elements in Cement, Slags and Feldspar S2 RANGER LE: Analysis of Light Elements in Cement, Slags and Feldspar 1 Welcome Today s topics: S2 RANGER LE o o o Overview XFlash LE detector Improved X-ray tube Analysis of Light Elements in Cement

More information

Steven L. Alderman, Michael S. Parsons, and Charles A. Waggoner. Institute for Clean Energy Technology, Mississippi State University

Steven L. Alderman, Michael S. Parsons, and Charles A. Waggoner. Institute for Clean Energy Technology, Mississippi State University The Effects of Media Velocity and Particle Size Distribution on Most Penetrating Particle Size and Filter Loading Capacity of 12 x12 x11.5 AG 1 HEPA Filters Steven L. Alderman, Michael S. Parsons, and

More information

Air Quality Monitoring at Dublin Airport: Annual Report for HSSE Department

Air Quality Monitoring at Dublin Airport: Annual Report for HSSE Department Air Quality Monitoring at Dublin Airport: Annual Report for 2013 Air Quality Monitoring at Dublin Airport: 2013 Table of Contents Glossary... 3 Executive Summary... 4 1. Introduction... 5 1.1. Background...

More information

The assessment is based upon the design ore production of 95 million tonnes / annum.

The assessment is based upon the design ore production of 95 million tonnes / annum. 9A Air Quality Assessment Supporting Information This annex sets out the detailed methodology, input data and criteria for the assessment. The overarching assessment approach is detailed in Chapter 9:

More information

Filtration Standards and Applications. Arkansas Chapter of ASHRAE December 6 & 7, 2006

Filtration Standards and Applications. Arkansas Chapter of ASHRAE December 6 & 7, 2006 Filtration Standards and Applications Arkansas Chapter of ASHRAE December 6 & 7, 2006 Outline Important Aspects of Particulate Filters Particulate Filter Test Standards Local Codes & Requirements Application

More information

THE MAP OF INDOOR RADON CONCENTRATIONS IN NORTHEASTERN ROMANIA

THE MAP OF INDOOR RADON CONCENTRATIONS IN NORTHEASTERN ROMANIA THE JOURNAL OF PREVENTIVE MEDICINE 2002; (3): -15 THE MAP OF INDOOR RADON CONCENTRATIONS IN NORTHEASTERN ROMANIA C. Grecea, Olga Iacob Institute of Public Health Iaşi Abstract. The radon concentrations

More information

History of Electrical Precipitation

History of Electrical Precipitation History of Electrical Precipitation Date 1600 1745 1824 1878 1885 Significance William Gilbert, English court physician, publishes De Magnete Benjamin Franklin describes the effects of points in drawing

More information

Calibration of Light Scatter PM-CEMs to Satisfy PS-11 on Wet Stacks in Coal Fired EGUs

Calibration of Light Scatter PM-CEMs to Satisfy PS-11 on Wet Stacks in Coal Fired EGUs Calibration of Light Scatter PM-CEMs to Satisfy PS-11 on Wet Stacks in Coal Fired EGUs William Averdieck, Ed McCall PCME Presented at EUEC 2015 1 Overview of Particulate Monitoring Experiences on Wet FGD

More information

Air Pollution & it s Effects. Presentation by: Dr. Gazala Habib Room 303, Block IV Department of Civil Engineering IIT Delhi

Air Pollution & it s Effects. Presentation by: Dr. Gazala Habib Room 303, Block IV Department of Civil Engineering IIT Delhi Air Pollution & it s Effects Presentation by: Dr. Gazala Habib Room 303, Block IV Department of Civil Engineering IIT Delhi Air Pollution Definition: Air pollution is the introduction of chemicals, particulate

More information

American International Journal of Research in Science, Technology, Engineering & Mathematics

American International Journal of Research in Science, Technology, Engineering & Mathematics American International Journal of Research in Science, Technology, Engineering & Mathematics Available online at http://www.iasir.net ISSN (Print): 2328-3491, ISSN (Online): 2328-358, ISSN (CD-ROM): 2328-3629

More information

Fluid Contamination Under Control...

Fluid Contamination Under Control... Fluid Contamination Under Control... DFE Rated Filter Element Upgrades Upgrade existing hydraulic and lube filter elements to Hy-Pro G7 Dualglass for cleaner fluid and improved reliability. Hy-Pro Elements

More information

ABSTRACT INTRODUCTION

ABSTRACT INTRODUCTION Simultaneous PM10 And PM2.5 Measurement From Stacks According to New ISO 23210 Standard Erkki J. Lamminen Dekati Ltd. Osuusmyllynkatu 13, 33700 Tampere, Finland ABSTRACT A new ISO standard 23210 for simultaneous

More information

A Home Use Study of Residential HVAC Filters

A Home Use Study of Residential HVAC Filters A Home Use Study of Residential HVAC Filters John Zhang and Andy Fox Construction and Home Improvement Markets Division Presentation in AFS 2015 October 7, 2015 Outline Characteristics of Residential HVAC

More information

Measuring Ytterbium Neutron Cross Section at 2.5 MeV. Norbert Hugger

Measuring Ytterbium Neutron Cross Section at 2.5 MeV. Norbert Hugger Project Number DM3 - AA9R Measuring Ytterbium Neutron Cross Section at 2.5 MeV A Major Qualifying Project Submitted to the Faculty of WORCESTER POLYTECHNIC INSTITUTE in partial fulfillment of the requirements

More information

Scientific & Technical Report

Scientific & Technical Report Scientific & Technical Report FCOSHOTEN Upgrade of Nuclear Power Plant Laundry Waste and Floor Drain Water Treatment System Utilizing Microfiltration 36th Annual Conference of the Canadian Nuclear Society

More information

Calibration Factors And Time-and-Distance Guidelines For Use of Theatrical Haze Equipment

Calibration Factors And Time-and-Distance Guidelines For Use of Theatrical Haze Equipment Calibration Factors And Time-and-Distance Guidelines For Use of Theatrical Haze Equipment Prepared for: CITC Everett, Washington Prepared by: ENVIRON International Corporation Westford, Massachusetts Date:

More information

Safety Assessment of Former Uranium Mine and Milling Facilities in Ukraine and Decommission Conception

Safety Assessment of Former Uranium Mine and Milling Facilities in Ukraine and Decommission Conception State Nuclear Regulatory Inspectorate of Ukraine Institute of geological sciences, National Academy of Sciences of Ukraine Safety Assessment of Former Uranium Mine and Milling Facilities in Ukraine and

More information

Thirty-Sixth Quarterly Report of Ambient Air Quality Monitoring at Sunshine Canyon Landfill and Van Gogh Elementary School

Thirty-Sixth Quarterly Report of Ambient Air Quality Monitoring at Sunshine Canyon Landfill and Van Gogh Elementary School Thirty-Sixth Quarterly Report of Ambient Air Quality Monitoring at Sunshine Canyon Landfill and Van Gogh Elementary School September 1, 2016 November 30, 2016 Quarterly Report STI-915023-6647-QR Prepared

More information

On-line determination of particle size and concentration (solids and oil) using ViPA Analyser - A way forward to control sub sea separators

On-line determination of particle size and concentration (solids and oil) using ViPA Analyser - A way forward to control sub sea separators Title On-line determination of particle size and concentration (solids and oil) using ViPA Analyser - A way forward to control sub sea separators Authors Dr. Kami Nezhati, Senior Development Engineer,

More information

PM Compliance Options for MACT and MATS Rules. Ed McCall PCME

PM Compliance Options for MACT and MATS Rules. Ed McCall PCME PM Compliance Options for MACT and MATS Rules Ed McCall PCME 1 First Some Definitions: PM- CEM, PM-CPMS and BLDs PM-CEM (PM- Continuous Emission Monitor) PM-CPMS (PM-Continuous Parametric Monitoring System)

More information

T8-1 [166 marks] Which energy resource is renewable? A. Natural gas B. Uranium C. Biogas D. Coal

T8-1 [166 marks] Which energy resource is renewable? A. Natural gas B. Uranium C. Biogas D. Coal T8-1 [166 marks] 1. Which energy resource is renewable? A. Natural gas B. Uranium C. Biogas D. Coal 2. For a black-body at absolute temperature T the power emitted per unit area is P. What is the power

More information

: Industrial Boiler MACT: CEM Requirements. Dan Kietzer: SICK Process Automation

: Industrial Boiler MACT: CEM Requirements. Dan Kietzer: SICK Process Automation : Industrial Boiler MACT: CEM Requirements Dan Kietzer: SICK Process Automation : Overview: Boiler MACT : Testing Boiler MACT Testing and Monitoring Requirement - Initial compliance tests (PM, HCl, Mercury,

More information

Radon and LBC at the Homestake Mine

Radon and LBC at the Homestake Mine Radon and LBC at the Homestake Mine Keenan Thomas 28 August 2010 LRT2010 1 Instruments Started (in earnest) in May 09 Instruments on loan from various institutions and labs. o 2-3 Rad7 s (USD, Brown, BNL)

More information

Filtration for Improved Bearing and Equipment Life Filtration for Improved Bearing and Equipment Life

Filtration for Improved Bearing and Equipment Life Filtration for Improved Bearing and Equipment Life Filtration for Improved Bearing Martin Williamson KEW Engineering Ltd. Bearings can have an infinite life when particles larger than the lubricant film are removed. SKF 2 3 4 Case Studies & Successes Nippon

More information

The e!ects of covering materials on indoor Rn concentrations in o$ces in Hong Kong

The e!ects of covering materials on indoor Rn concentrations in o$ces in Hong Kong Journal of Environmental Radioactivity 47 (2000) 183}188 The e!ects of covering materials on indoor Rn concentrations in o$ces in Hong Kong K.N. Yu*, T. Cheung, E.C.M. Young, W.N. Mui, K.K. Tang Department

More information

Can your unit pass a Particulate Emission Compliance Test?

Can your unit pass a Particulate Emission Compliance Test? Source Emissions Testing and Emissions Specialists Can your unit pass a Particulate Emission Compliance Test? Kevin Crosby The Avogadro Group, LLC California - Oregon - Arizona McIlvaine Hot Topic Hour,

More information

2008 Beltwide Cotton Conferences, Nashville, Tennessee, January 8-11, 2008

2008 Beltwide Cotton Conferences, Nashville, Tennessee, January 8-11, 2008 546 UPDATE ON THE FIELD EVALUATION OF EPA METHOD CTM-039 (PM2.5 STACK SAMPLING METHOD) Michael D. Buser USDA-ARS Cotton Production and Processing Research Unit Lubbock, TX Derek P. Whitelock USDA-ARS,

More information

MMEA D Results of the feasibility studies for combustion and diesel exhaust gas measurements

MMEA D Results of the feasibility studies for combustion and diesel exhaust gas measurements MMEA D4.5.1.5 Results of the feasibility studies for combustion and diesel exhaust gas measurements V1 March 211 DEKATI Ltd Contractors DEKATI Ltd. Osuusmylynkatu 13 FIN-337 Tampere FINLAND TTY säätiö

More information

STANDARDIZED FILTER TESTS OF METAL WORKING FLUID MIST SEPARATORS

STANDARDIZED FILTER TESTS OF METAL WORKING FLUID MIST SEPARATORS STANDARDIZED FILTER TESTS OF METAL WORKING FLUID MIST SEPARATORS Dipl.-Ing. Thomas Laminger Mechanical Process Engineering and Clean Air Technology CONTENT Introduction Background information about Metal

More information

Measurement of Individual Radon Progeny in Egyptian Under Ground Coal Mine and Related Lung Doses

Measurement of Individual Radon Progeny in Egyptian Under Ground Coal Mine and Related Lung Doses Egypt. J. Solids, Vol. (29), No. (2), (2006) 383 Measurement of Individual Radon Progeny in Egyptian Under Ground Coal Mine and Related Lung Doses M. Abd El-Hady Physics Department, Faculty of Science,

More information

Performance Standards for Indicative Ambient Particulate Monitors Environment Agency July 2012 Version 2

Performance Standards for Indicative Ambient Particulate Monitors Environment Agency July 2012 Version 2 Performance Standards for Indicative Ambient Particulate Monitors Environment Agency July 2012 Version 2 Foreword We set up our Monitoring Certification Scheme (MCERTS) to provide a framework of standards

More information

Thirty-Seventh Quarterly Report of Ambient Air Quality Monitoring at Sunshine Canyon Landfill and Van Gogh Elementary School

Thirty-Seventh Quarterly Report of Ambient Air Quality Monitoring at Sunshine Canyon Landfill and Van Gogh Elementary School Thirty-Seventh Quarterly Report of Ambient Air Quality Monitoring at Sunshine Canyon Landfill and Van Gogh Elementary School December 1, 2016 February 28, 2017 Quarterly Report STI-915023-6716-QR Prepared

More information

Physical, Chemical and Electrical Analysis of Dust Generated from Cement Plants for Dust Removal with an Electrostatic Precipitator

Physical, Chemical and Electrical Analysis of Dust Generated from Cement Plants for Dust Removal with an Electrostatic Precipitator Korean J. Chem. Eng., 21(1), 182-186 (2004) Physical, Chemical and Electrical Analysis of Dust Generated from Cement Plants for Dust Removal with an Electrostatic Precipitator Young-Chull Ahn, Jae-Min

More information

New Approaches to Quantitative Proteomics Analysis

New Approaches to Quantitative Proteomics Analysis New Approaches to Quantitative Proteomics Analysis Chris Hodgkins, Market Development Manager, SCIEX ANZ 2 nd November, 2017 Who is SCIEX? Founded by Dr. Barry French & others: University of Toronto Introduced

More information

How safe is Beijing s Air Quality for Human Health? Naresh Kumar Θ

How safe is Beijing s Air Quality for Human Health? Naresh Kumar Θ How safe is Beijing s Air Quality for Human Health? Naresh Kumar Θ Abstract: The success of the 2008 Olympics will be largely impacted by the level of air pollution in Beijing. The World Health Organization

More information

MODELING THE SPREAD OF ANTHRAX IN BUILDINGS

MODELING THE SPREAD OF ANTHRAX IN BUILDINGS MODELING THE SPREAD OF ANTHRAX IN BUILDINGS RG Sextro *, DM Lorenzetti, MD Sohn, and TL Thatcher Indoor Environment Dept., Lawrence Berkeley National Lab, Berkeley, CA, USA ABSTRACT The recent contamination

More information

Risk Assessment from Radon Gas in the Greenhouses

Risk Assessment from Radon Gas in the Greenhouses Risk Assessment from Radon Gas in the Greenhouses N. M. Fahmi a, M. Abd el-zaher b, A. M. El-Khatib a a- Physics Department, Faculty of Science, Alexandria University, Egypt b-department of Basic and Applied

More information

Leadership in Filtration. ScandMist Industrial air cleaners

Leadership in Filtration. ScandMist Industrial air cleaners Leadership in Filtration ScandMist Industrial air cleaners ScandMist For clean and safe workshop environments THE PROBLEM THE ANSWER Industrial processes that combine lubricant with high-speed machine

More information

APPENDIX 4C ISS PUMPOUT ANALYSIS

APPENDIX 4C ISS PUMPOUT ANALYSIS 2020 Facilities Plan Treatment Report APPENDIX 4C ISS PUMPOUT ANALYSIS Notes No. Storm Event 1 Average Total ISS Pump 1 Pump 2 Pump 3 (MGD) Average Individual Pumpout Per Storm Event Pumpout 2 1 8/4/1998

More information

Preliminary Field Evaluation of EPA Method CTM-039 (PM2.5 Stack Sampling Method) Michael D. Buser and Derek P. Whitelock

Preliminary Field Evaluation of EPA Method CTM-039 (PM2.5 Stack Sampling Method) Michael D. Buser and Derek P. Whitelock Preliminary Field Evaluation of EPA Method CTM-039 (PM2.5 Stack Sampling Method) Michael D. Buser and Derek P. Whitelock ABSTRACT Agricultural operations are encountering difficulties complying with current

More information

STANDARDIZED FILTER TESTS OF METAL WORKING FLUID MIST SEPARATORS

STANDARDIZED FILTER TESTS OF METAL WORKING FLUID MIST SEPARATORS STANDARDIZED FILTER TESTS OF METAL WORKING FLUID MIST SEPARATORS Dipl.-Ing. Thomas Laminger Univ. Prof. Dr. Wilhelm Höflinger Mechanical Process Engineering and Clean Air Technology TEMPUS MEETING VIENNA

More information

Application Note. Raman Spectroscopy Analysis of Crystalline Polymorphs for Pharmaceutical Development

Application Note. Raman Spectroscopy Analysis of Crystalline Polymorphs for Pharmaceutical Development Raman Applications in the Pharmaceutical Industry Impurity Analysis (Identification of micro impurities - sizes less than 1 µm) Evaluation of Synthetized Compounds (Structural analysis in combination with

More information

Practical implementation of anticipated radon dosimetry changes in the mining industry

Practical implementation of anticipated radon dosimetry changes in the mining industry International Conference on Occupational Radiation Protection: Enhancing the Protection of Workers Gaps, Challenges and Developments Vienna, Austria, 1-5 December 2014 Practical implementation of anticipated

More information

Evaluation of the resuspension factor for radiological contaminants in conditions of spent nuclear fuel transports from nuclear plants

Evaluation of the resuspension factor for radiological contaminants in conditions of spent nuclear fuel transports from nuclear plants Evaluation of the resuspension factor for radiological contaminants in conditions of spent nuclear fuel transports from nuclear plants A. Douce, D. Hameau, C. Letoffe, G. Morel, F. Saintamon, C. Penoty

More information

Experimental study assessment of mitigation of carbon formation on Ni/YSZ and Ni/CGO SOFC anodes operating on gasification syngas and tars

Experimental study assessment of mitigation of carbon formation on Ni/YSZ and Ni/CGO SOFC anodes operating on gasification syngas and tars Experimental study assessment of mitigation of carbon formation on Ni/YSZ and Ni/CGO SOFC anodes operating on gasification syngas and tars Clean Coal Technologies Conference 2009 19 May 2009 Joshua Mermelstein

More information

The Leader in Performance Indoor Air Quality Measurements

The Leader in Performance Indoor Air Quality Measurements The Leader in Performance Indoor Air Quality Measurements ENERGY AND COMFORT TRUST. SCIENCE. INNOVATION. Breathe a Little Easier with TSI Indoor air quality is a growing concern. With the increasing amount

More information

Quality Control of Drilled Piles

Quality Control of Drilled Piles Quality Control of Drilled Piles (Drilled Shafts, Bored Piles, Augercast piles) Garland Likins, P.E. Pile Dynamics, Inc. August 2015 2015, Pile Dynamics, Inc. For a pile to successfully carry the required

More information

A LOW PRESSURE DROP SINTERED METAL FILTER FOR ULTRA-HIGH PURITY GAS SYSTEMS

A LOW PRESSURE DROP SINTERED METAL FILTER FOR ULTRA-HIGH PURITY GAS SYSTEMS A LOW PRESSURE DROP SINTERED METAL FILTER FOR ULTRA-HIGH PURITY GAS SYSTEMS Dr. Kenneth L. Rubow Donna S. Prause, Mark Eisenmann Mott Corporation Presented at the 3 rd Annual Technical Meeting Institute

More information

Brachytherapy Practice Problems EXTRA

Brachytherapy Practice Problems EXTRA Brachytherapy Practice Problems EXTRA 1. 100 mci decays to 12.5 mci in days, if the half-life is 17d. a. 170 b. 136 c. 85 d. 51 e. 25 2. A radionuclide has a half-life of 74 d. The activity after 370 days

More information

ESTCP Research on Optimization of Vapor Intrusion Mitigation Systems in Large Military Buildings

ESTCP Research on Optimization of Vapor Intrusion Mitigation Systems in Large Military Buildings ESTCP Research on Optimization of Vapor Intrusion Mitigation Systems in Large Military Buildings Todd McAlary, Ph.D., P.Eng., P.G., CUT Principal and Practice Leader Vapor Intrusion Services Geosyntec

More information

Dispersion of Respirable Particles Emitted from Surface Mining Operations

Dispersion of Respirable Particles Emitted from Surface Mining Operations 15 th International Conference on Environmental Science and Technology Rhodes, Greece, 31 August to 2 September 2017 Dispersion of Respirable Particles Emitted from Surface Mining Operations Sahu S. P.

More information

New prototype prefilter for seawater RO

New prototype prefilter for seawater RO Techneau January 2007 New prototype prefilter for seawater RO Protocol for bench-scale testing Techneau January 2007 New prototype prefilter for seawater RO Protocol for bench-scale testing 2006 is an

More information

High-energy x-ray production with pyroelectric crystals

High-energy x-ray production with pyroelectric crystals JOURNAL OF APPLIED PHYSICS 97, 104916 2005 High-energy x-ray production with pyroelectric crystals Jeffrey A. Geuther a and Yaron Danon Department of Mechanical, Aerospace, and Nuclear Engineering, Rensselaer

More information

Factors Affecting Suspended Particulate Matter Concentration in Multi-storied Buildings

Factors Affecting Suspended Particulate Matter Concentration in Multi-storied Buildings International Journal of Environmental Research and Development. ISSN 2249-3131 Volume 4, Number 3 (2014), pp. 227-232 Research India Publications http://www.ripublication.com/ijerd.htm Factors Affecting

More information

CEE 370 Environmental Engineering Principles

CEE 370 Environmental Engineering Principles Updated: 19 November 2015 Print version CEE 370 Environmental Engineering Principles Lecture #29 Water Treatment III: Softening, Settling, Filtration Reading: M&Z Chapter 8 Reading: Davis & Cornwall, Chapt

More information

WM2014 Conference, March 2 6, 2014, Phoenix, Arizona, USA

WM2014 Conference, March 2 6, 2014, Phoenix, Arizona, USA Air Sample Conditioner Helps the Waste Treatment Plant Meet Emissions Standards 14646 John Glissmeyer *, Julia Flaherty *, Mikhail Pekour * * Pacific Northwest National Laboratory ABSTRACT The air in three

More information

Filter Clogging by Bimodal Aerosol

Filter Clogging by Bimodal Aerosol Aerosol Science and Technology, 40:255 260, 2006 Copyright c American Association for Aerosol Research ISSN: 0278-6826 print / 1521-7388 online DOI: 10.1080/02786820500543282 Filter Clogging by Bimodal

More information

MEAN ANNUAL EXPOSURE OF CHILDREN AGED 0-4 YEARS TO ATMOSPHERIC PARTICULATE POLLUTION

MEAN ANNUAL EXPOSURE OF CHILDREN AGED 0-4 YEARS TO ATMOSPHERIC PARTICULATE POLLUTION MEAN ANNUAL EXPOSURE OF CHILDREN AGED 0-4 YEARS TO ATMOSPHERIC PARTICULATE POLLUTION GENERAL CONSIDERATIONS Issues Type of indicator Rationale Issues in indicator design Respiratory disease Exposure (proximal)

More information

EFFECTS OF EMISSIONS ON CURRENT AND FUTURE RAINFALL PATTERNS IN SOUTHEAST BRAZIL

EFFECTS OF EMISSIONS ON CURRENT AND FUTURE RAINFALL PATTERNS IN SOUTHEAST BRAZIL EFFECTS OF EMISSIONS ON CURRENT AND FUTURE RAINFALL PATTERNS IN SOUTHEAST BRAZIL UNESP: Institute of Chemistry, Araraquara (Arnaldo Cardoso) Institute of Meteorological Research, Bauru (Gerhard Held) USP:

More information

What is Aero microbiology?

What is Aero microbiology? AEROMICROBIOLOGY What is Aero microbiology? Aero microbiology is the study of living microbes which are suspended in the air. These microbes are referred to as bio aerosols. There are significantly less

More information

Ambient Air Monitoring Systems

Ambient Air Monitoring Systems Ambient Air Monitoring Systems ECM ambient air monitoring systems are integrated in air conditioned thermal isolated light weight shelters allowing stationary and mobile installations. The usually monitored

More information

ABSTRACT INTRODUCTION

ABSTRACT INTRODUCTION 1 Developing a System-Level Monitoring Instrument for UV-Curing Systems Dr. Peyman H. Dehkordi, James L. Riner, and Douglas E. Ingram Applied Computing Technology, Inc. 1010D Commerce Park Drive Oak Ridge,

More information

Microfil GP. Range. Validation Guide. World Class Filtration Solutions

Microfil GP. Range. Validation Guide. World Class Filtration Solutions Microfil GP Range Validation Guide World Class Filtration Solutions Contents Microfil GP Range Validation Guide Introduction 3 - Construction Microfil GP Materials of Construction 4 - FDA Approval - Dimensions

More information

Health impacts of air pollution in London: from understanding to forecasting

Health impacts of air pollution in London: from understanding to forecasting Health impacts of air pollution in London: from understanding to forecasting John Gulliver University of the West of Scotland Marta Blangiardo, David Briggs, Anna Hansell Imperial College London Study

More information

Compact flue gas analyser: testo 300 M-I

Compact flue gas analyser: testo 300 M-I 220 Compact flue gas analyser: testo 300 M-I PC analysis Prints Small memory -------------------- testo 300-I -------------------- 16.07.2001 09:36:22 C Quick flue gas checks are of interest for all industrial

More information

Controlling Emissions and Saving Money with Highly Engineered Cartridge Filter Technology

Controlling Emissions and Saving Money with Highly Engineered Cartridge Filter Technology Controlling Emissions and Saving Money with Highly Engineered Cartridge Filter Technology Introduction By Richard Lydon, VP Technology & Business Development Over the last number of years Clear Edge has

More information