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Silver Nanoparticles,
the environment and your health-
What do we know, and what do we need to know
Dr. Dearbháile Morris
Antimicrobial Resistance and Microbial Ecology Group,
School of Medicine, and
Ryan Institute, Centre for Health from Environment
NUI Galway
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
Dr. Dearbháile Morris Dr. Enda Cummins Dr. Andrew Fogarty Dr. Patrick Dunlop
Dr. Eoin McGillicuddy Mr. David Shevlin Mr. Iain Murray
Dr. Liam Morrison
Prof. Martin Cormican
Prof. Peter Dockery
http://www.epa.ie/pubs/reports/research/health/research259.html
“A natural, incidental or manufactured material containing particles, in an unbound
state or as an aggregate or as an agglomerate and where, for 50 % or more of the
particles in the number size distribution, one or more external dimensions is in the
size range
1 nm - 100 nm”.
(2011/696/EU).
What are nanoparticles?
Source: Bhattachajee , C. et al. Austin Chem Eng. 2016; 3(3): 1036
• Nanoparticles can be naturally occurring,
inadvertently generated and engineered.
• Engineered nanomaterials (ENMs) are intentionally
produced, and exhibit unique properties.
Source: Larson, Jeremy & Carvan, Michael & Hutz, Reinhold. (2014). Engineered Nanomaterials: An Emerging Class of Novel Endocrine Disruptors.
Biology of reproduction. 91. 10.1095/biolreprod.113.116244.
What are nanoparticles?
What are nanoparticles used for?
Household products Personal Care products
Medical Applications Soil and Water Remediation
Textiles and Others
Why focus on Silver nanoparticles?
Silver has been used for centuries due to its antibacterial properties
Why focus on Silver nanoparticles?
• The annual global consumption of nanosilver has been
estimated to be between 55 1 - 4502 ton/year
• Potential for AgNP release during manufacture, use
and disposal of the nano-functionalised products
• Studies have found that some nano-functionalised
textiles can release up to 100% of its nanosilver during
washing
1 Piccinno, F., Gottschalk, F., Seeger, S., Nowack, B., 2012. Industrial Production Quantities and Uses of ten Engineered Nanomaterials in Europe and the World.
2 Future Markets, Inc.; The Global Market for Nanomaterials 2002−2016: Production Volumes, Revenues and End Use Markets; 2012; p 371.
http://www.futuremarketsinc.com.
ENMs are safe to use.......right??
Source: Teow, Y. et al. Chem. Commun., 2011,47, 7025-7038
http://dx.doi.org/10.1039/C0CC05271J
• Concern that the unique properties
of ENMs may result in potential
hazards for both humans and the
environment.
• Nanoparticles can be released into
various environmental matrices such
as soil, sediment, air and water
during their production, use and
disposal.
• Nanoparticles pose a potential risk
to human health through ingestion,
inhalation and contact
• The REACH (Registration, Evaluation and Authorization of
Chemicals)regulations (Regulation (EC) No. 1907/2006)......no consensus
as to how REACH applies to ENMs.
• The Scientific Knowledge for Environmental Protection (SKEP)
Nanomaterials in REACH Report1 concluded that most REACH
provisions and assessment tools are not appropriate to evaluate
the safety of nanomaterials.
1SKEP. 2011. SKEP Nanomaterials in REACH Report. www.skep-network.eu/SKEP_Nanomaterials_in_REACH_Report
ENMs are safe to use.......right??
Manufacturers and importers of nanomaterials (NMs) should be
required to register any variation of their NM(s) prior to
commercialisation and independent of production and import
volumes.
All uses of NMs should be evaluated according to the NanoRiskCat
methodology
Obligation on companies to declare the quantities and uses
of substances at nanoscale produced, distributed or
imported to ANSES.
Belgium, Denmark and Norway have also initiated similar
inventories of products.
Italy, Germany, Sweden and the U.K. are proposing to
introduce some form of regulation.
Regulation of ENMs in Europe
Ireland?
• Evidence is lacking and safe levels have not been established.
• Several studies provide evidence that nanoparticles in consumer
products can accumulate in water the majority of studies to date rely on
modelling data.
• Lack of monitoring and detection data, or an agreed methodology for
nanoparticle monitoring in waters and other environmental matrices.
• Lack of data in the scientific literature regarding the toxicity of silver
nanoparticles in natural raw water.
4DEHLG and Camp. Dresser and McKee Ltd. (2004). Economic Analysis of Water use in Ireland. http://www.wfdireland.ie/docs/35_Economics/Economic%20Analysis%20of%20Water%20use.pdf
What impact do AgNps have on human health
and the environment?
1. To develop and implement a method for the detection,
characterisation and quantification of silver nanoparticles in water.
2. To determine the toxicological properties of silver nanoparticles in
the aquatic environment.
3. To develop risk assessment protocols which can be used to evaluate
the environmental fate and likely risk from silver nanoparticles
through aquatic pathways.
Aims:
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
Detection
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
Charcoal is a commonly used as an adsorbant in water purification.
Granulated Ground Milled
Detection
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
76.28%
65.89%
94.12% 89.92%
0
20
40
60
80
100
100 ppb 10 nm
citrate coated
100 ppb 25 nm
PVP coated
10 ppb 10 nm
citrate coated
10 ppb 25 nm PVP
coated
%Agremovedfromsample
Comparison of AgNP capture by charcoal using AgNPs
with different sizes and coatingsActivated charcoal is a suitable material for capture of
AgNPs from water.
Potential as a cost-effective material for the capture and
remediation of AgNPs, and possibly other nano-wastes,
from the aquatic environment.
Toxicology
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
Primary Producer
Pseudokirchnerriella
subcapitata
Primary Consumer
Daphnia magna
Secondary Consumer
Hydra attenuata
Multi-trophic test battery
Toxicology
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
An EDTA-free medium should be utilised to improve test
sensitivity .
The effect of Ag on the regeneration of Hydra attenuata is
the most environmentally relevant bioassay investigated.
Risk Assessment
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
Risk Assessment
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
• Current models estimate predicted environmental concentrations
of AgNP to be in the low ng L-1 range
• Low risk to human health based on predicted environmental
concentrations.
• For the scenarios considered, there is no existing risk from AgNPs
residues following drinking of water.
Key Recommendations
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
 An Irish national inventory of all products containing nanoparticles
should be established and updated on a regular basis.
 Further investigations should be carried out to determine the levels of
AgNPs in the Irish environment. These studies should allow for
examination of their impacts on the environment and associated risks.
Key Recommendations
DeTER
Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles
in the aquatic environment (2014-HW-MS-1)
 This study substantiates the need for international bodies to
develop and harmonise a suite of ecotoxicology bioassays for the
risk assessment of Ag nanomaterials.
 Given the rapid uptake of nanotechnology in various sectors, and
the consequential likely increased environmental release of
ENMs, environmental and human exposure will change and
should be constantly monitored and re-evaluated.
Acknowledgements
Environmental Protection Agency for funding under EPA Research
Programme 2014–2020
Project Team
Project Steering Committee:
• Dr. Brian Quinn (UWS)
• Dr. Aisling O’Connor (EPA)
• Dr. Brian Donlon (EPA)
• Dr. Alan Stephens (EPA)
• Dr. Rachel Clarke (EPA)
DUBLIN, MAY 22ND -24TH 2019
TEAGASC CONFERENCECENTRE,ASHTOWN,DUBLIN
JOINTLY HOSTEDBY NUI GALWAY ANDTEAGASC

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Annual environment and health conference 2018 speaker7 dearbhaile morris_deter_project

  • 1. Silver Nanoparticles, the environment and your health- What do we know, and what do we need to know Dr. Dearbháile Morris Antimicrobial Resistance and Microbial Ecology Group, School of Medicine, and Ryan Institute, Centre for Health from Environment NUI Galway
  • 2. DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1) Dr. Dearbháile Morris Dr. Enda Cummins Dr. Andrew Fogarty Dr. Patrick Dunlop Dr. Eoin McGillicuddy Mr. David Shevlin Mr. Iain Murray Dr. Liam Morrison Prof. Martin Cormican Prof. Peter Dockery
  • 4. “A natural, incidental or manufactured material containing particles, in an unbound state or as an aggregate or as an agglomerate and where, for 50 % or more of the particles in the number size distribution, one or more external dimensions is in the size range 1 nm - 100 nm”. (2011/696/EU). What are nanoparticles? Source: Bhattachajee , C. et al. Austin Chem Eng. 2016; 3(3): 1036
  • 5. • Nanoparticles can be naturally occurring, inadvertently generated and engineered. • Engineered nanomaterials (ENMs) are intentionally produced, and exhibit unique properties. Source: Larson, Jeremy & Carvan, Michael & Hutz, Reinhold. (2014). Engineered Nanomaterials: An Emerging Class of Novel Endocrine Disruptors. Biology of reproduction. 91. 10.1095/biolreprod.113.116244. What are nanoparticles?
  • 6. What are nanoparticles used for? Household products Personal Care products Medical Applications Soil and Water Remediation Textiles and Others
  • 7.
  • 8. Why focus on Silver nanoparticles? Silver has been used for centuries due to its antibacterial properties
  • 9.
  • 10. Why focus on Silver nanoparticles? • The annual global consumption of nanosilver has been estimated to be between 55 1 - 4502 ton/year • Potential for AgNP release during manufacture, use and disposal of the nano-functionalised products • Studies have found that some nano-functionalised textiles can release up to 100% of its nanosilver during washing 1 Piccinno, F., Gottschalk, F., Seeger, S., Nowack, B., 2012. Industrial Production Quantities and Uses of ten Engineered Nanomaterials in Europe and the World. 2 Future Markets, Inc.; The Global Market for Nanomaterials 2002−2016: Production Volumes, Revenues and End Use Markets; 2012; p 371. http://www.futuremarketsinc.com.
  • 11. ENMs are safe to use.......right?? Source: Teow, Y. et al. Chem. Commun., 2011,47, 7025-7038 http://dx.doi.org/10.1039/C0CC05271J • Concern that the unique properties of ENMs may result in potential hazards for both humans and the environment. • Nanoparticles can be released into various environmental matrices such as soil, sediment, air and water during their production, use and disposal. • Nanoparticles pose a potential risk to human health through ingestion, inhalation and contact
  • 12. • The REACH (Registration, Evaluation and Authorization of Chemicals)regulations (Regulation (EC) No. 1907/2006)......no consensus as to how REACH applies to ENMs. • The Scientific Knowledge for Environmental Protection (SKEP) Nanomaterials in REACH Report1 concluded that most REACH provisions and assessment tools are not appropriate to evaluate the safety of nanomaterials. 1SKEP. 2011. SKEP Nanomaterials in REACH Report. www.skep-network.eu/SKEP_Nanomaterials_in_REACH_Report ENMs are safe to use.......right??
  • 13.
  • 14.
  • 15. Manufacturers and importers of nanomaterials (NMs) should be required to register any variation of their NM(s) prior to commercialisation and independent of production and import volumes. All uses of NMs should be evaluated according to the NanoRiskCat methodology
  • 16.
  • 17.
  • 18.
  • 19. Obligation on companies to declare the quantities and uses of substances at nanoscale produced, distributed or imported to ANSES. Belgium, Denmark and Norway have also initiated similar inventories of products. Italy, Germany, Sweden and the U.K. are proposing to introduce some form of regulation. Regulation of ENMs in Europe
  • 21. • Evidence is lacking and safe levels have not been established. • Several studies provide evidence that nanoparticles in consumer products can accumulate in water the majority of studies to date rely on modelling data. • Lack of monitoring and detection data, or an agreed methodology for nanoparticle monitoring in waters and other environmental matrices. • Lack of data in the scientific literature regarding the toxicity of silver nanoparticles in natural raw water. 4DEHLG and Camp. Dresser and McKee Ltd. (2004). Economic Analysis of Water use in Ireland. http://www.wfdireland.ie/docs/35_Economics/Economic%20Analysis%20of%20Water%20use.pdf What impact do AgNps have on human health and the environment?
  • 22. 1. To develop and implement a method for the detection, characterisation and quantification of silver nanoparticles in water. 2. To determine the toxicological properties of silver nanoparticles in the aquatic environment. 3. To develop risk assessment protocols which can be used to evaluate the environmental fate and likely risk from silver nanoparticles through aquatic pathways. Aims: DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1)
  • 23. Detection DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1) Charcoal is a commonly used as an adsorbant in water purification. Granulated Ground Milled
  • 24. Detection DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1) 76.28% 65.89% 94.12% 89.92% 0 20 40 60 80 100 100 ppb 10 nm citrate coated 100 ppb 25 nm PVP coated 10 ppb 10 nm citrate coated 10 ppb 25 nm PVP coated %Agremovedfromsample Comparison of AgNP capture by charcoal using AgNPs with different sizes and coatingsActivated charcoal is a suitable material for capture of AgNPs from water. Potential as a cost-effective material for the capture and remediation of AgNPs, and possibly other nano-wastes, from the aquatic environment.
  • 25. Toxicology DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1) Primary Producer Pseudokirchnerriella subcapitata Primary Consumer Daphnia magna Secondary Consumer Hydra attenuata Multi-trophic test battery
  • 26. Toxicology DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1) An EDTA-free medium should be utilised to improve test sensitivity . The effect of Ag on the regeneration of Hydra attenuata is the most environmentally relevant bioassay investigated.
  • 27. Risk Assessment DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1)
  • 28. Risk Assessment DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1) • Current models estimate predicted environmental concentrations of AgNP to be in the low ng L-1 range • Low risk to human health based on predicted environmental concentrations. • For the scenarios considered, there is no existing risk from AgNPs residues following drinking of water.
  • 29. Key Recommendations DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1)  An Irish national inventory of all products containing nanoparticles should be established and updated on a regular basis.  Further investigations should be carried out to determine the levels of AgNPs in the Irish environment. These studies should allow for examination of their impacts on the environment and associated risks.
  • 30. Key Recommendations DeTER Detection, Toxicology, Environmental fate and Risk assessment of silver nanoparticles in the aquatic environment (2014-HW-MS-1)  This study substantiates the need for international bodies to develop and harmonise a suite of ecotoxicology bioassays for the risk assessment of Ag nanomaterials.  Given the rapid uptake of nanotechnology in various sectors, and the consequential likely increased environmental release of ENMs, environmental and human exposure will change and should be constantly monitored and re-evaluated.
  • 31.
  • 32. Acknowledgements Environmental Protection Agency for funding under EPA Research Programme 2014–2020 Project Team Project Steering Committee: • Dr. Brian Quinn (UWS) • Dr. Aisling O’Connor (EPA) • Dr. Brian Donlon (EPA) • Dr. Alan Stephens (EPA) • Dr. Rachel Clarke (EPA)
  • 33. DUBLIN, MAY 22ND -24TH 2019 TEAGASC CONFERENCECENTRE,ASHTOWN,DUBLIN JOINTLY HOSTEDBY NUI GALWAY ANDTEAGASC

Editor's Notes

  1. Wide range of applications, from everyday uses, eg, household products to medical applications, water and soil remediation and renewable energy production. The production and demand for products containing nanomaterials has increased significantly in recent years
  2. Within Europe, France has been the leader in terms of governmental regulation of nanomaterials. Articles L. 523–1 to L. 523–3 of the French Environment Code oblige companies to declare the quantities and uses of substances at nanoscale produced, distributed or imported to ANSES (the French agency for food safety, the environment and labour) (Ministry of Ecology, Sustainable Development, Transport and Housing, 2012). Belgium, Denmark and Norway have also initiated similar inventories of products whereas other countries such as Italy, Germany, the UK and Sweden are proposing to introduce some form of regulation (Anses, 2014; KEMI, 2015; ChemicalWatch, 2016; Hansen et al., 2016). Currently, in Ireland there is a lack of knowledge across sectors on the quantities and uses of substances at nanoscale. The development of an Irish national inventory in line with other European countries is warranted.
  3. Persian kings such as Cyrus the Great carried water supplies in silver vessels to prevent it from becoming contaminated when going to war. The Macedonians used silver plates to improve wound healing and Hippocrates used silver in the treatment of ulcers. C.S.F. Crede used eye drops containing one-percent silver nitrate solution to treat eye infections in new-borns Silver dollars were placed into buckets of milk by American pioneers to prevent milk from spoiling
  4. Persian kings such as Cyrus the Great carried water supplies in silver vessels to prevent it from becoming contaminated when going to war. The Macedonians used silver plates to improve wound healing and Hippocrates used silver in the treatment of ulcers. C.S.F. Crede used eye drops containing one-percent silver nitrate solution to treat eye infections in new-borns Silver dollars were placed into buckets of milk by American pioneers to prevent milk from spoiling
  5. Although nanomaterials are covered by these regulations as chemicals, there are not any nanospecific regulations (EC, 2006). Some current European regulations do have relevance to products containing nanomaterials. These include the biocidal products regulation [Regulation (EU) No. 528/2012], regulation on cosmetic products [Regulation (EC) No. 1223/2009], regulation on the provision of food information to consumers [Regulation (EU) No. 1169/2011], regulation on plastic materials and articles intended to come into contact with food [Regulation (EU) No. 10/2011], regulation related to novel foods [Regulation (EU) No. 2015/2283], Regulation (EC) No. 1333/2008 on food additives and Regulation (EU) No. 2017/745 on medical devices (SCENIHR, 2014; Rauscher et al., 2017).Within Europe, France has been the leader in terms of governmental regulation of nanomaterials. Articles L. 523–1 to L. 523–3 of the French Environment Code oblige companies to declare the quantities and uses of substances at nanoscale produced, distributed or imported to ANSES (the French agency for food safety,the environment and labour) (Ministry of Ecology,Sustainable Development, Transport and Housing,2012). Belgium, Denmark and Norway have also initiated similar inventories of products whereas other countries such as Italy, Germany, the UK and Sweden are proposing to introduce some form of regulation (Anses, 2014; KEMI, 2015; ChemicalWatch, 2016; Hansen et al., 2016). Currently, in Ireland there is a lack of knowledge across sectors on the quantities and uses of substances at nanoscale. The development of an Irish national inventory in line with other European countries is warranted.
  6. In an article published in the prestigious scientific journal, Nature Nanotechnology, Associate Professor Steffen Foss Hansen from DTU Environment calls for the adoption of a new regulatory framework for nanomaterials – REACT NOW. The framework is called REACT NOW which stands for Registration, Evaluation, Authorisation, Categorisation and Tools to Evaluate Nanomaterials – Opportunities and Weaknesses. Steffen Foss Hansen recommends that manufacturers and importers of nanomaterials (NMs) should be required to register any variation of their NM(s) prior to commercialisation and independent of production and import volumes. All uses of NMs should be evaluated according to the NanoRiskCat methodology that is also used in The Nanodatabase.
  7. In an article published in the prestigious scientific journal, Nature Nanotechnology, Associate Professor Steffen Foss Hansen from DTU Environment calls for the adoption of a new regulatory framework for nanomaterials – REACT NOW. The framework is called REACT NOW which stands for Registration, Evaluation, Authorisation, Categorisation and Tools to Evaluate Nanomaterials – Opportunities and Weaknesses. Steffen Foss Hansen recommends that manufacturers and importers of nanomaterials (NMs) should be required to register any variation of their NM(s) prior to commercialisation and independent of production and import volumes. All uses of NMs should be evaluated according to the NanoRiskCat methodology that is also used in The Nanodatabase.
  8. In an article published in the prestigious scientific journal, Nature Nanotechnology, Associate Professor Steffen Foss Hansen from DTU Environment calls for the adoption of a new regulatory framework for nanomaterials – REACT NOW. The framework is called REACT NOW which stands for Registration, Evaluation, Authorisation, Categorisation and Tools to Evaluate Nanomaterials – Opportunities and Weaknesses. Steffen Foss Hansen recommends that manufacturers and importers of nanomaterials (NMs) should be required to register any variation of their NM(s) prior to commercialisation and independent of production and import volumes. All uses of NMs should be evaluated according to the NanoRiskCat methodology that is also used in The Nanodatabase.
  9. In an article published in the prestigious scientific journal, Nature Nanotechnology, Associate Professor Steffen Foss Hansen from DTU Environment calls for the adoption of a new regulatory framework for nanomaterials – REACT NOW. The framework is called REACT NOW which stands for Registration, Evaluation, Authorisation, Categorisation and Tools to Evaluate Nanomaterials – Opportunities and Weaknesses. Steffen Foss Hansen recommends that manufacturers and importers of nanomaterials (NMs) should be required to register any variation of their NM(s) prior to commercialisation and independent of production and import volumes. All uses of NMs should be evaluated according to the NanoRiskCat methodology that is also used in The Nanodatabase.
  10. Within Europe, France has been the leader in terms of governmental regulation of nanomaterials. Articles L. 523–1 to L. 523–3 of the French Environment Code oblige companies to declare the quantities and uses of substances at nanoscale produced, distributed or imported to ANSES (the French agency for food safety, the environment and labour) (Ministry of Ecology, Sustainable Development, Transport and Housing, 2012). Belgium, Denmark and Norway have also initiated similar inventories of products whereas other countries such as Italy, Germany, the UK and Sweden are proposing to introduce some form of regulation (Anses, 2014; KEMI, 2015; ChemicalWatch, 2016; Hansen et al., 2016). Currently, in Ireland there is a lack of knowledge across sectors on the quantities and uses of substances at nanoscale. The development of an Irish national inventory in line with other European countries is warranted.
  11. Within Europe, France has been the leader in terms of governmental regulation of nanomaterials. Obligation on companies to declare the quantities and uses of substances at nanoscale produced, distributed or imported to ANSES (the French agency for food safety,t he environment and labour). Belgium, Denmark and Norway have also initiated similar inventories of products. Italy, Germany, the UK and Sweden are proposing to introduce some form of regulation. Currently, in Ireland there is a lack of knowledge across sectors on the quantities and uses of substances at nanoscale.
  12. Currently, in Ireland there is a lack of knowledge across sectors on the quantities and uses of substances at nanoscale
  13. Evidence is lacking regarding the potential impact AgNps present in consumer products have on human health or the environment and safe levels have not been established.
  14. Charcoal is a commonly used material in water purification where it is used as an adsorbant Previous study successfully used charcoal as an adsorbant for 60 nm citrate coated nanoparticles (Gicheva and Yordanov, 2013) Previous study added electrolytes in order to improve AgNP removal Charcoal used for out study was Norit CA1 activated charcoal which is used in water purification
  15. Charcoal is a commonly used material in water purification where it is used as an adsorbant Previous study successfully used charcoal as an adsorbant for 60 nm citrate coated nanoparticles (Gicheva and Yordanov, 2013) Previous study added electrolytes in order to improve AgNP removal Charcoal used for out study was Norit CA1 activated charcoal which is used in water purification
  16. Charcoal is a commonly used material in water purification where it is used as an adsorbant Previous study successfully used charcoal as an adsorbant for 60 nm citrate coated nanoparticles (Gicheva and Yordanov, 2013) Previous study added electrolytes in order to improve AgNP removal Charcoal used for out study was Norit CA1 activated charcoal which is used in water purification
  17. Charcoal is a commonly used material in water purification where it is used as an adsorbant Previous study successfully used charcoal as an adsorbant for 60 nm citrate coated nanoparticles (Gicheva and Yordanov, 2013) Previous study added electrolytes in order to improve AgNP removal Charcoal used for out study was Norit CA1 activated charcoal which is used in water purification
  18. Charcoal is a commonly used material in water purification where it is used as an adsorbant Previous study successfully used charcoal as an adsorbant for 60 nm citrate coated nanoparticles (Gicheva and Yordanov, 2013) Previous study added electrolytes in order to improve AgNP removal Charcoal used for out study was Norit CA1 activated charcoal which is used in water purification
  19. Charcoal is a commonly used material in water purification where it is used as an adsorbant Recent survey of the Isar River, Germany found increased levels of AgNPs at WWTP discharge points (2.0−8.6 ng L−1) with much lower levels found 1.5 km downstream (0.9−2.3 ng L−1)1 Previous study successfully used charcoal as an adsorbant for 60 nm citrate coated nanoparticles (Gicheva and Yordanov, 2013) Previous study added electrolytes in order to improve AgNP removal Charcoal used for out study was Norit CA1 activated charcoal which is used in water purification
  20. Charcoal is a commonly used material in water purification where it is used as an adsorbant Recent survey of the Isar River, Germany found increased levels of AgNPs at WWTP discharge points (2.0−8.6 ng L−1) with much lower levels found 1.5 km downstream (0.9−2.3 ng L−1)1 Previous study successfully used charcoal as an adsorbant for 60 nm citrate coated nanoparticles (Gicheva and Yordanov, 2013) Previous study added electrolytes in order to improve AgNP removal Charcoal used for out study was Norit CA1 activated charcoal which is used in water purification
  21. Charcoal is a commonly used material in water purification where it is used as an adsorbant Recent survey of the Isar River, Germany found increased levels of AgNPs at WWTP discharge points (2.0−8.6 ng L−1) with much lower levels found 1.5 km downstream (0.9−2.3 ng L−1)1 Previous study successfully used charcoal as an adsorbant for 60 nm citrate coated nanoparticles (Gicheva and Yordanov, 2013) Previous study added electrolytes in order to improve AgNP removal Charcoal used for out study was Norit CA1 activated charcoal which is used in water purification