18.03.2013Eivind Farmen Giftighet av nanosølv for fisk I norske vann og vassdrag 1.

Slides:



Advertisements
Similar presentations
3/25/2017 Social Jessica Winters
Advertisements

A 2030 framework for climate and energy policies Marten Westrup
Some Transport Types Simple diffusion (Down a chemical or electrical potential gradient) Facilitated diffusion (Down a chemical or electrical potential.
Chemical Quantities or
Angstrom Care 培苗社 Atoms II
Chapter 7 Chemical Quantities
1 Copyright © 2013 Elsevier Inc. All rights reserved. Chapter 38.
The Plasma Membrane - Gateway to the Cell.
Product Safety Governance
The Future of Metals Center for Industrial Ecology Thomas E. Graedel
Jeopardy Q 1 Q 6 Q 11 Q 16 Q 21 Q 2 Q 7 Q 12 Q 17 Q 22 Q 3 Q 8 Q 13
Jeopardy Q 1 Q 6 Q 11 Q 16 Q 21 Q 2 Q 7 Q 12 Q 17 Q 22 Q 3 Q 8 Q 13
Balancing Equations Practice Sheet. 1. __ NaOH + __ Pb(NO 3 ) 2 -->__ NaOH 3 + __ Pb(OH) 2 List metals, non-metals, then H and O.
1 Zentrum für Umweltforschung und nachhaltige Technologien Prof. Dr. Jorg Thöming, June 2012.
ZMQS ZMQS
Aquatic & Fisheries Ecology. Aquatic = taking place in or on water Fishery = the occupation, industry, or season of taking fish or other aquatic animals.
Minneapolis – St. Paul Visitor Count and Profile
Chemistry An Introduction to General, Organic, and Biological Chemistry, Eleventh Edition Copyright © 2012 by Pearson Education, Inc. Chapter 5 Chemical.
Solubility and Complex-Ion Equilibria
Degradation of organic micropollutants via Advanced Oxidation Process (UV/H 2 O 2 ) Josanne Derks Results pilot plant research.
Evaluation of photothermal effects induced by laser heating of gold nanorods in suspensions and inoculated tumors G.S. Terentyuk, D.S. Chumakov, I.L. Maksimova.
Metallic and Ionic Nanoparticles
Lecture – 6 Dr. Zahoor Ali Shaikh
15. Oktober Oktober Oktober 2012.
Strong Acids/ Bases Strong Acids more readily release H+ into water, they more fully dissociate H2SO4  2 H+ + SO42- Strong Bases more readily release.
Lets play bingo!!. Calculate: MEAN Calculate: MEDIAN
TRANSPORT ACROSS CELL MEMBRANE-II
1. What does this symbol mean? 2. Sodium has this hazard symbol - what precautions should you take when using it?
Sandia National Laboratories is a multi-program laboratory managed and operated by Sandia Corporation, a wholly owned subsidiary of Lockheed Martin Corporation,
Addition 1’s to 20.
25 seconds left…...
Mark, Set, ….Go!. 1) Biology is the study of 2) A testable explanation of an observation.
Week 1.
We will resume in: 25 Minutes.
Figure Essential Cell Biology (© Garland Science 2010)
1 Unit 1 Kinematics Chapter 1 Day
Entry Task: Jan 25 th Friday Question: Identify the acid, base and conjugate acid and conjugate base when nitric acid reacts with sodium hydroxide. You.
Dosimetry in Risk Assessment and a bit More Mel Andersen McKim Conference QSAR and Aquatic Toxicology & Risk Assessment June 27-29, 2006.
Michael Yip BIO 464 TuTh 2 – 3:15.  High electrical/thermal conductivity, surface- enhanced Raman scattering, chemical stability, catalytic activity,
Problem/Challenge hematite in cosmetics Naturally occurring, incidental, and manufactured NPs are of different sizes and nanomorphologies. Which are more.
Biology 201 Dr. Edwin DeMont St. Francis Xavier University Body Fluid Regulation.
POLYCHLORINATED BIPHENYLS (PCBs) By Jenn Corpuz. PHYSICAL & CHEMICAL PROPERTIES C 12 H 10-x Cl x MP: C Thin, lightly colored liquids to yellow.
and Environmental Risk Assessment
Nanoparticles in the environment – how small is the risk? Anders Baun Nanna Hartmann Khara Grieger Michael Andersen Steffen Foss Hansen.
LOGO Neurobehavioral Effect of Nanosilver in Adult Male Offsprings Technical Workshop for the Asia-Pacific Region on Nanosafety Issues, Sept 2015,
Results Fig. 4 The Ag measured in DGT devices (left), and body burden of silver in the deposit- feeding polychaete, Capitella teleta (right). Note that.
BLOOD CELLS METABOLISM. Objectives of the Lecture 1- Understanding the general structural & functional features of red blood cells (RBCs). 2- Recognizing.
1 Selecting Materials for Understanding the Human Health and Ecological Risks of Nanomaterials Considerations and Approach Justin Teeguarden, PhD., DABT.
THE NEED FOR NANOMATERIAL EVALUATION IN A PHYSIOLOGICALLY RELEVANT MODEL: CONNECTING ENVIRONMENTAL VARIABLES AND NM BEHAVIOR TO TOXICOLOGICAL RESPONSES.
22 October 2014 Claudia Moia Early Stage Researcher, Cranfield University (UK) Cell type- and size- dependent in vitro toxicity of silica particles in.
Silver Nanoparticle and Ecotoxicology Research Some Uncertainties
Physicochemical transformations of ZnO NPs under aging process in aquatic environment and the toxicity to green algae Hefei Institutes of Physical Science,
McKim Conference on Predictive Toxicology The Inn of Lake Superior Duluth, Minnesota September 25-27, 2007 Toxicity Pathways as an Organizing Concept Gilman.
Nanomaterialer – udgør de et miljø- og sundhedsmæssigt problem? Steffen Foss Hansen, Laura Roverskov Heggelund, Pau Revilla Besora, Aiga Mackevica, Alessio.
Importance of surface modification of silica nanoparticles, exposure conditions and particle uptake for cytokine responses in epithelial lung cells. NANOMAT.
Health and environmental impacts of nanoparticles: too early for a risk assessment framework? Prof Jim Bridges Emeritus Professor of Toxicology and Environmental.
Mechanisms involved in cytokine responses induced by carbon black nanoparticles in epithelial lung cells Annike Irene Totlandsdal Department of Air Pollution.
University College Dublin School of Biosystems Engineering Migration Assessment of Nanosilver Coated Low Density Polyethylene with Potential Application.
Patricia Gillis Copper Sensitivity in Glochidia: Assessing the Effect of Water Composition on the Sensitive Larvae of Freshwater Mussels.
University of Koblenz-Landau, Germany
Temporal Thin Film Stability Studies Using Silver Nanoparticles
Z. Gajda-Meissner, M. Hartl, T. F. Fernandes
Typha capensis—An Electron Rich Resource For The Synthesis of Phytochemical-Encapsulated Gold Nanoparticles Through Green Nanotechnology Keenau Pearce1,4,5,
(A) Schematic description of working principle and detection scheme.
Can Wastewater Treatment Plants (WWTPs) cope with future nanoparticles (ENPs) loading scenarios? Valerio Cappadonaa, Rebecca Skuceb, Charles Knappa, Vernon.
Palacký University in Olomouc
Toxicological Analysis of Silver Nanoparticles and Colistin coated AgNp using Drosophila as a model organism” Dr. Ravish H Assistant Professor, Department.
Proximal tubule HCO3− reabsorption and H+ secretion.
Excretion The removal of metabolic waste from the body. e.g. carbon dioxide and urea Where do these come from?
Presentation transcript:

Eivind Farmen Giftighet av nanosølv for fisk I norske vann og vassdrag 1

Eivind Farmen2 Silver - the most common material used in commercial nano-products

Nanosilver from a washing machine Concentration in effluent: 2,7 µg/L to 25 µg/L Average: 10,522 µg/L Large variability! Particles found with TEM: Size range: 6 – 11 nm Farkas (2011) Environment international 37 (6),

Objectives Determine acute and sublethal toxicity of AgNP to fish & fish cells Determine AgNP characteristics in various matrixes Compare toxic potential of AgNP to ionic silver and AuNP Assess risk to fish under ecologicaly relevant exposure scenarios Eivind Farmen

In vitro experimental model What are the possible effects of nanoparticles on fish cells used as an in vitro test system? Liver Gill Exposure (48h) Cytotoxicity Reactive oxygen species (ROS) production Epithelial integrity Primary hepatocytes Primary gill epithelium cells Eivind Farmen

Particle characteristics by TEM AgNPs Water cell media cell media +DOC Roundish to oval particle shape AuNPs In–house synthesized citrate-coated NPs

ROS production & Cytotoxicity (hepatocytes) Silver NPs Gold NPs ROS Cytotoxicity Farkas et al Effects of silver and gold nanoparticles on rainbow trout (Oncorhynchus mykiss) hepatocytes. Aquatic toxicol Eivind Farmen

Effects on primary gill cells Ag is less cytotoxic to gill cells than to hepatocytes AuNPs were not cytotoxic Eivind Farmen

Eivind Farmen What happens in natural water? Commercial AgNP 1:10 in natural lake water In-house AgNP 1:10 in natural lake water 4 nm 220 nm 9

Effects Ag nanoparticles ? ? Control 1  g/L AgNP 20  g/L AgNP 100  g/L AgNP 20  g/L Ag+ 100  g/L AgNP Eivind Farmen10

Eivind Farmen GO analysis AgNP 20 µg/L 11

Eivind Farmen GO analysis 12

Transcriptional UP-regulation (Ag) 100 ug/L AgNP20 ug/L Ag+ 20 ug/L AgNP Heme-binding protein 2 Protein-Glutamine  -glutamyltransferase GTPase IMAP family member 4 Na/H exchanger Eivind Farmen13

Transcriptional Down-regulation (Ag) 100 ug/L AgNP20 ug/L Ag+ 20 ug/L AgNP Carbonic anhydrase 7 Na/K-ATPase Interferon gamma MHC Class II Eivind Farmen14

Mode of action Ag BloodGillWater HCO 3 - Cl - NaK- ATPase H + (NH 4 + ) Na + K+K+ Carbonic anhydrase CO 2 + H 2 O => H + + HCO 3 - CO 2 Na + K+K+ Cl - CO Eivind Farmen15

Hazard/risk assessment 100 ug/L AgNP 20 ug/L Ag + 20 ug/L AgNP Control Toxicity of AgNP due to acting as reservoir for Ag + ? Toxicity of AgNP higher in soft waters ! Eivind Farmen16

Effects Ag nanoparticles Control 1  g/L AgNP 20  g/L AgNP 100  g/L AgNP 20  g/L AgNP 100  g/L AgNP Eivind Farmen17 Osmo- regulation Necrosis/ apoptosis

Work in progress Eivind Farmen18

Differences Ag-NPs Eivind Farmen19

Eivind Farmen Conclusion High toxicity of Ag-NPs in natural Norwegian waters Ag-NP effect mediated by Ag+ ions? Effects in gills/osmoregulation Modulation of immune system Effect in gills > liver 20

Eivind Farmen Acknowledgements Farkas J, Mikkelsen HN, Evensen Ø, Heier LS, Einset J, Salbu B, Rosseland BO, Oughton DH, Tollefsen KE, Paul Christian, Julián Alberto Gallego-Urrea, Norbert Roos, Martin Hassellöv, Kevin V Thomas, Mie Jareid, Hanne Fossnes, Hans-Christian Teien Funding: – Norwegian Research Council » Nanotrace Project » NIVA, SIP project NEWPOLL Thank you for listening! 21