Information Catalog: Release Measurement Studies
Release Measurement Studies
Summary: Part B
Carbon Nanotubes |
| Release Method |
Measurement Methods |
Release Characterization |
Statistics |
References |
| band saw, or rotary cutting wheel |
xxx, SEM & TEM |
dry cutting: 71-89% (1-10mm), 6-25% (0.1-1mm) & 1-10% (<100nm): no identifiable CNT fibers or bundles |
|
Bello et al. (2009) |
| band saw, or rotary cutting wheel |
xxx, SEM & TEM |
dry cutting: 71-89% (1-10mm), 6-25% (0.1-1mm) & 1-10% (<100nm): no identifiable CNT fibers or bundles |
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Bello et al. (2009) |
| Reference Links |
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Additional study details are available in Summary: Part A. |
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Graphite Sheet |
| Release Method |
Measurement Methods |
Release Characterization |
Statistics |
References |
| unspecified "fire like" heat flux |
TEM |
no release reported: conformational change reported - delaminated to intercalated structure |
|
Nyden and Gilman (1998) |
| Reference Links |
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Additional study details are available in Summary: Part A. |
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Carbon Nanofibers |
| Release Method |
Measurement Methods |
Release Characterization |
Statistics |
References |
| flame temperature in excess of 1200C |
unspecified |
no release in smoke: nanoparticle release from char at 6,000mm2/cm3 - 14,000mm2/cm3 |
|
Nyden and Uddin (n.d.) |
| Reference Links |
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- Nyden and Uddin (n.d.) Presentation.
Additional study details are available in Summary: Part A. |
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Carbon Black |
| Release Method |
Measurement Methods |
Release Characterization |
Statistics |
References |
| Hand held orbital sander (Metabo model FSR 200): grit size 240 paper |
aerosol particle sizer (APS; model 3321), Fast Mobility Particle Sizer (FMPS: model 3091) |
no individual particles were observed, 5 modes of particles were emitted: <50nm particles were mostly form the sander motor, ~200nm were sander emitted and paint dust, >1mm dust particles from paints regardless of carbon black |
3-5 modal fitted log-normal distributions were fitted to measured emissions |
Koponen et al. (2009) |
| Reference Links |
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Additional study details are available in Summary: Part A. |
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Titania |
| Release Method |
Measurement Methods |
Release Characterization |
Statistics |
References |
| Hand held orbital sander (Metabo model FSR 200): grit size 240 paper |
aerosol particle sizer (APS; model 3321), Fast Mobility Particle Sizer (FMPS: model 3091) |
no individual particles were observed, 5 modes of particles were emitted: <50nm particles were mostly form the sander motor, ~200nm were sander emitted and paint dust, >1mm dust particles from paints regardless of nano-titania |
3-5 modal fitted log-normal distributions were fitted to measured emissions |
Koponen et al. (2009) |
| (2x) two hour exposures to: fluorescent lamp or 5 UV lamps (l=365nm & P=50mW), s, fan (75m/min) & rubber knife (1min every 10min) |
scanning mobility particle scanner (SMPS) |
Most particle emission was <200nm, the highest concentration 50-150nm, under all conditions; UV light caused considerably more release then fluorescent lamps; release from tile continued to increase over the 2 hr testing |
|
Hsu and Chein (2007) |
| (2x) two hour exposures to: fluorescent lamp or 5 UV lamps (l=365nm & P=50mW), s, fan (75m/min) & rubber knife (1min every 10min) |
scanning mobility particle scanner (SMPS) |
Most particle emission was <200nm, the highest concentration 50-150nm, under all conditions; UV light caused considerably more release then fluorescent lamps; release from tile continued to increase over the 2 hr testing |
|
Hsu and Chein (2007) |
| (2x) two hour exposures to: fluorescent lamp or 5 UV lamps (l=365nm & P=50mW), s, fan (75m/min) & rubber knife (1min every 10min) |
scanning mobility particle scanner (SMPS) |
Most particle emission was <200nm, the highest concentration 50-150nm, under all conditions; UV light caused considerably more release then fluorescent lamps; release from tile continued to increase over the 2 hr testing |
|
Hsu and Chein (2007) |
| Natural rain in urban environment, collected as runoff & urban discharge |
SEM, TEM (CM30, source LaB6, FEI) with EDX, environmental scanning electron microscope (ESEM), high-resolution scanning electron microscope (HR-SEM), Inductive coupled plasma optical transmission (ICP-OES) & mass spectrometry (ICP-MS) |
release of isolated, agglomerate and embedded in carrier matrix synthetic TiO2 particles (85-90% in 20-300nm range) detected from new and aged model facades, and in urban runoff; greater release from new compared to aged facades |
|
Kaegi et al. (2008) |
| Reference Links |
|
- Hsu, L. and H. Chein (2007) Evaluation of nanoparticles emission for TiO2 nanopowder coating materials. Journal of Nanoparticle Research. 9:157-163.
- Kaegi, R., A. Ulrich, B. Sinnet, R. Vonbank, A. Wichser, S. Zuleeg, H. Simmler, S. Brunner, H. Vonmont, M. Burkhardt and M. Boller (2008) Synthetic TiO2 nanoparticle emission from exterior facades into the aquatic environment. Environmental Pollution. 156: 233-239.
- Koponen, I., K. Jensen and T. Schneider (2009) Sanding dust from nanoparticles-containing paints: physical characterization. Journal of Physics, Conference Series (Inhaled Particles X). 151: 1-9.
Additional study details are available in Summary: Part A. |
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Zinc Oxide |
| Release Method |
Measurement Methods |
Release Characterization |
Statistics |
References |
| Taber Abraser: 2.5N, CS-17 rolls, 3 cycles of 100 rotations |
scanning mobility particle scanner (SMPS; model 3934), condensation particle counter (CPC model 3022) & TEM |
detectable, but insignificant release from all carrier systems, no correlation between nanomaterial doping and <650nm or <100nm release: n-ZnO found embedded within released wear particles |
three tests run to ensure a detection probability of 95% according to the Poisson-statistic |
Vorbau et al. (2009) |
| Taber Abraser: 2.5N, CS-17 rolls, 3 cycles of 100 rotations |
scanning mobility particle scanner (SMPS; model 3934), condensation particle counter (CPC model 3022) & TEM |
detectable, but insignificant release from all carrier systems, no correlation between nanomaterial doping and <650nm or <100nm release: n-ZnO found embedded within released wear particles |
three tests run to ensure a detection probability of 95% according to the Poisson-statistic |
Vorbau et al. (2009) |
| Taber Abraser: 2.5N, CS-17 rolls, 3 cycles of 100 rotations |
scanning mobility particle scanner (SMPS; model 3934), condensation particle counter (CPC model 3022) & TEM |
detectable, but insignificant release from all carrier systems, no correlation between nanomaterial doping and <650nm or <100nm release: n-ZnO found embedded within released wear particles |
three tests run to ensure a detection probability of 95% according to the Poisson-statistic |
Vorbau et al. (2009) |
| Taber Abraser: 2.5N, CS-17 rolls, 3 cycles of 100 rotations |
scanning mobility particle scanner (SMPS; model 3934), condensation particle counter (CPC model 3022) & TEM |
detectable, but insignificant release from all carrier systems, no correlation between nanomaterial doping and <650nm or <100nm release: n-ZnO found embedded within released wear particles |
three tests run to ensure a detection probability of 95% according to the Poisson-statistic |
Vorbau et al. (2009) |
| Dremel (Model series 400) contact force 0.2-1N; contact pressure 0.0004 - 50,000Pa; speed 1.8-2.4m/s-1 |
Fast Mobility Particle Sizer (FMPS: model 3091), Laser aerosol particle size spectrometer (LAP; model 321), condensation particle counter (CPC model 3022), APS, TEM & SEM |
All samples released particles <100nm, and release was uncorrelated with doping of nanoparticles. Paint with n-ZnO doped paint released 10nm and 100nm. Under SEM, no free n-ZnO particles were identified, all were found embedded in the paint wear particles. |
|
Göhler et al. (2010) |
| Dremel (Model series 400) contact force 0.2-1N; contact pressure 0.0004 - 50,000Pa; speed 1.8-2.4m/s-1 |
Fast Mobility Particle Sizer (FMPS: model 3091), Laser aerosol particle size spectrometer (LAP; model 321), condensation particle counter (CPC model 3022), APS, TEM & SEM |
All samples released particles <100nm, and release was uncorrelated with doping of nanoparticles. Paint with n-ZnO doped paint released 10nm and 100nm. Under SEM, no free n-ZnO particles were identified, all were found embedded in the paint wear particles. |
|
Göhler et al. (2010) |
| Dremel (Model series 400) contact force 0.2-1N; contact pressure 0.0004 - 50,000Pa; speed 1.8-2.4m/s-1 |
Fast Mobility Particle Sizer (FMPS: model 3091), Laser aerosol particle size spectrometer (LAP; model 321), condensation particle counter (CPC model 3022), APS, TEM & SEM |
All samples released particles <100nm, and release was uncorrelated with doping of nanoparticles. Paint with n-ZnO doped paint released 10nm and 100nm. Under SEM, no free n-ZnO particles were identified, all were found embedded in the paint wear particles. |
|
Göhler et al. (2010) |
| Dremel (Model series 400) contact force 0.2-1N; contact pressure 0.0004 - 50,000Pa; speed 1.8-2.4m/s-1 |
Fast Mobility Particle Sizer (FMPS: model 3091), Laser aerosol particle size spectrometer (LAP; model 321), condensation particle counter (CPC model 3022), APS, TEM & SEM |
All samples released particles <100nm, and release was uncorrelated with doping of nanoparticles. Paint with n-ZnO doped paint released 10nm and 100nm. Under SEM, no free n-ZnO particles were identified, all were found embedded in the paint wear particles. |
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Göhler et al. (2010) |
| Reference Links |
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Additional study details are available in Summary: Part A. |
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Iron Oxide |
| Release Method |
Measurement Methods |
Release Characterization |
Statistics |
References |
| Dremel (Model series 400) contact force 0.2-1N; contact pressure 0.0004 - 50,000Pa; speed 1.8-2.4 m/s-1 |
FMPS, CPC & SEM |
All samples released particles <100nm, and release was uncorrelated with doping of nanoparticles. Paint with n-Fe2O3 released more nanoparticles around 10nm and 25nm. Under SEM, no free n-Fe2O3 particles were identified, all were found embedded in paint wear particles. |
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Göhler et al. (2010) |
| Reference Links |
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Additional study details are available in Summary: Part A. |
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Silver |
| Release Method |
Measurement Methods |
Release Characterization |
Statistics |
References |
| 500 ml of ultra-pure water in amber bottle; 3x(1 or 24 hrs) on orbital shaker at 50 rpm |
inductively coupled plasma optical emission spectroscopy, filtration, ion selective electrode (ISE) & SEM |
initial n-Ag content in socks ranged from undetectable - 1,358.8 mg n-Ag/g sock; Ag release ranged from 0.5% - 100%; about 70-90% of silver release was ionic; SEM analysis showed released n-Ag appears like initial n-Ag. |
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Benn and Westerhoff (2008) |
| City of Tempe tap water: 1 hr on orbital shaker at 50 rpm |
filtration & SEM |
medical mask contained the most n-Ag initially (25% of product weight) but released the least 0.1%; shirt released the most ~2%; filtration of release n-Ag, 2/3 or more <100nm, 1/3 <20nm; SEM showed particles <20nm and 200-500nm agglomerates |
|
Benn et al. (2010) |
| artificial sweat (ISO 105-EO4-2008E (@ pH 5.5 & 8.0); BS EN1811-1999; AATCC #15-2002) soaking for 24 hrs @ 37C |
Graphite furnace atomic absorption spectroscopy (GFAAS: Perkin-Elmer Analyst 300) |
concentration dependent release of n-Ag in lab prepared fabrics, far less and variable release from commercial fabrics |
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Kulthong et al. (2010) |
| Two different methods used: (1) ISO 105-C06: 1997 for 30min @ 40C & pH 7; (2) mild agitation in buffered pH 10 solution for 120min, then addition of oxidizing agents: per acetic acid (PAA) or H2O2. |
ISE (Metrohm 6.0726.100); ICP-OES (Perkin-Elmer); LM 20 Nanosight; X-ray fluorescence spectroscopy |
Minimal n-Ag released under pH10 conditions (70% Ag+ & 30% >450nm). During washing ~1% of the total n-Ag content was released as (90% >450nm, 2% <450nm & 3% Ag+) |
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Geranio et al. (2009) |
| Two different methods used: (1) ISO 105-C06: 1997 for 30min @ 40C & pH 7; (2) mild agitation in buffered pH 10 solution for 120min, then addition of oxidizing agents: per acetic acid (PAA) or H2O2. |
ISE (Metrohm 6.0726.100); ICP-OES (Perkin-Elmer); LM 20 Nanosight; X-ray fluorescence spectroscopy |
About 10% of toal n-Ag released under pH10 conditions (5%>450nm, 50% <450nm & 65% Ag+). During washing ~18% of the total n-Ag content was released as (38% >450nm, 12% <450nm & 50% Ag+) |
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Geranio et al. (2009) |
| Two different methods used: (1) ISO 105-C06: 1997 for 30min @ 40C & pH 7; (2) mild agitation in buffered pH 10 solution for 120min, then addition of oxidizing agents: per acetic acid (PAA) or H2O2. |
ISE (Metrohm 6.0726.100); ICP-OES (Perkin-Elmer); LM 20 Nanosight; X-ray fluorescence spectroscopy |
About 5% of total n-Ag released under pH10 conditions (48% >450nm & 52% <450nm). During washing 33% of the total n-Ag content was released as (82% >450nm, 18% <450nm ) |
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Geranio et al. (2009) |
| Two different methods used: (1) ISO 105-C06: 1997 for 30min @ 40C & pH 7; (2) mild agitation in buffered pH 10 solution for 120min, then addition of oxidizing agents: per acetic acid (PAA) or H2O2. |
ISE (Metrohm 6.0726.100); ICP-OES (Perkin-Elmer); LM 20 Nanosight; X-ray fluorescence spectroscopy |
About 3% of total n-Ag released under pH10 conditions (40% >450nm & 60% <450nm). During washing ~20% of the total n-Ag content was released as (75% >450nm & 25% <450nm ) |
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Geranio et al. (2009) |
| Two different methods used: (1) ISO 105-C06: 1997 for 30min @ 40C & pH 7; (2) mild agitation in buffered pH 10 solution for 120min, then addition of oxidizing agents: per acetic acid (PAA) or H2O2. |
ISE (Metrohm 6.0726.100); ICP-OES (Perkin-Elmer); LM 20 Nanosight; X-ray fluorescence spectroscopy |
About 13% of total n-Ag released under pH10 conditions (20% >450nm & 80% Ag+). During washing ~35% of the total n-Ag content was released as (82% >450nm, 15% <450nm & 3% Ag+) |
|
Geranio et al. (2009) |
| Two different methods used: (1) ISO 105-C06: 1997 for 30min @ 40C & pH 7; (2) mild agitation in buffered pH 10 solution for 120min, then addition of oxidizing agents: per acetic acid (PAA) or H2O2. |
ISE (Metrohm 6.0726.100); ICP-OES (Perkin-Elmer); LM 20 Nanosight; X-ray fluorescence spectroscopy |
About 3% n-Ag released under pH10 conditions (100% >450nm). During washing ~2% of the total n-Ag content was released as (100% >450nm) |
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Geranio et al. (2009) |
| Two different methods used: (1) ISO 105-C06: 1997 for 30min @ 40C & pH 7; (2) mild agitation in buffered pH 10 solution for 120min, then addition of oxidizing agents: per acetic acid (PAA) or H2O2. |
ISE (Metrohm 6.0726.100); ICP-OES (Perkin-Elmer); LM 20 Nanosight; X-ray fluorescence spectroscopy |
About 2% n-Ag released under pH10 conditions (50% >450nm & 50% <450nm). During washing ~3% of the total n-Ag content was released as (80% >450nm & 20% <450nm) |
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Geranio et al. (2009) |
| Two different methods used: (1) ISO 105-C06: 1997 for 30min @ 40C & pH 7; (2) mild agitation in buffered pH 10 solution for 120min, then addition of oxidizing agents: per acetic acid (PAA) or H2O2. |
ISE (Metrohm 6.0726.100); ICP-OES (Perkin-Elmer); LM 20 Nanosight; X-ray fluorescence spectroscopy |
About 8% n-Ag released under pH10 conditions (100% >450nm). |
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Geranio et al. (2009) |
| Two different methods used: (1) ISO 105-C06: 1997 for 30min @ 40C & pH 7; (2) mild agitation in buffered pH 10 solution for 120min, then addition of oxidizing agents: per acetic acid (PAA) or H2O2. |
ISE (Metrohm 6.0726.100); ICP-OES (Perkin-Elmer); LM 20 Nanosight; X-ray fluorescence spectroscopy |
About 25% of total n-Ag released under pH10 conditions (95% Ag+ & 5% >450nm). During washing ~15% of the total n-Ag content was released as (90% >450nm, 8% <450nm & 2% Ag+) |
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Geranio et al. (2009) |
| Reference Links |
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- Benn, T. and P. Westerhoff (2008) Nanoparticle silver released into water from commercially available sock fabrics. Environmental Science and Technology. 42: 4133-4139.
- Benn, T., B. Cavanagh, K. Hristovski, J. Posner and P. Westerhoff (2010) The release of nanosilver from consumer products used in the home. Journal of Environmental Quality. 39: 1875-1882.
- Geranio, L., M. Heuberger and B. Nowack (2009) The behavior of silver nanotextiles during washing. Environmental Science and Technology. 43: 8113-8118.
- Kulthong, K., S. Srisung, K. Boonpavanitchakul, W. Kangwansupamonkon and R. Maniratanachote (2010) Determination of silver nanoparticle release from antibacterial fabrics into artificial sweat. Particle Fibre Toxicology. 7: 8.
Additional study details are available in Summary: Part A. |
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