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Grantee Research Project Results

Final Report: Innate Immune Response of an Aquatic Vertebrate Model to Manufactured Nanoparticles Assessed Using Genomic Markers

EPA Grant Number: R833319
Title: Innate Immune Response of an Aquatic Vertebrate Model to Manufactured Nanoparticles Assessed Using Genomic Markers
Investigators: Klaper, Rebecca , Goetz, Frederick , Chen, Jian
Institution: University of Wisconsin - Madison
EPA Project Officer: Hahn, Intaek
Project Period: April 1, 2008 through April 15, 2011
Project Amount: $398,810
RFA: Exploratory Research: Nanotechnology Research Grants Investigating Environmental and Human Health Effects of Manufactured Nanomaterials: a Joint Research Solicitation-EPA, NSF, NIOSH, NIEHS (2006) RFA Text |  Recipients Lists
Research Category: Nanotechnology , Safer Chemicals

Objective:

The overall objective of this project is to assess the innate immune reaction of an aquatic model, the rainbow trout, to manufactured nanomaterials of varying chemistries at levels not inducing cellular toxicity. This research will create a mechanism with which to test other nanomaterials, provide data to support ecological risk assessments, and ultimately inform decisions as to which materials will be the safest to industrialize and use with respect to aquatic environments.

Summary/Accomplishments (Outputs/Outcomes):

During the first year of this project, we focused on creating our first set of nanomaterials, fullerenes with varying functional groups that were positively, negatively, or neutrally charged and had differing structural attachments (covalently or not covalently functionalized). We then used these materials to probe our immune model system. Our investigations have focused on testing a wide concentration range (0.1-100 ug/mL) for each nanomaterial to determine toxicity to macrophage cells using two tests for cytotoxicity: (1) the metabolic reduction of resazurin and (2) lactate dehydrogenase activity (LDH). The goal was to determine if these particles were cytotoxic and at what concentration. In addition, this information was then used as a range finding experiment to determine the concentrations to use for determining the impact on immune function. We wanted a concentration where we would see immune stimulation but not see a complete destruction of the cellular system. We used concentrations of nanomaterials below cytotoxic levels to test for effects on targeted gene expression. We chose TNFα (tumor necrosis factor) and COX2 (cyclooxygenase) as representative of proinflammatory genes; IFNα (interferon) and IP-10 (interferon inducible protein) as genes associated with the antiviral response; and IL10 (interleukin) and TGFβ-1 (transforming growth factor) as representative of the antiinflammatory (alternative/Th2) pathway. Each gene was assayed for expression in several tissue concentrations using RT-PCR (QPCR) to investigate any dose-dependent effects on expression.
 
In the second year of our project, we continued creating nanomaterials with differing functionalization by including single and multi-walled carbon nanomaterials. We narrowed our candidate genes down to ILl and IFN as the best indicators of inflammatory and antiviral responses. These were used to screen all further nanomaterials.
 
In the final years of this project, we focused on a narrow set of concentrations of nanomaterials and those that caused the greatest immune response (single walled nanotubes with varying functionalization) and used custom microarrays to determine if there were unique genomic signatures associated with each nanomaterial exposure. In addition, we examined whether genomic response provided an indication as to whether the nanomaterials were differing in their immune effects based on their structure or functionalization.
 
Achievements with respect to stated goals:
 
Our goals for this project have been completely aligned with what we have accomplished. The overall goals of this project were to assess the innate immune reaction of an aquatic vertebrate, the rainbow trout (Oncorhynchus mykiss), to the in vitro exposure of macrophages to engineered nanomaterials, and to create a mechanism to test other types of nanomaterials by developing immunological testing procedures, including the development of genomic biomarkers, to evaluate the effects of exposure. More specifically, our goals were to:
 
i. Determine the viability of in vitro macrophage cultures for a dose range of each type of nanomaterial to be tested for gene expression.
 
Our findings:
 
We found that cells remain viable with doses of nanomaterials up to 100 ug/mL of nanomaterials for all nanomaterials tested (fullerenes, fullerenes with various functional groups, single walled nanotubes and multiwalled nanotubes included those that have been modified to be water soluble), which is quite high. This indicates that cells remain intact and functioning in the presence of nanomaterial exposures and that overall nanomaterials may be impacting the physiology of a cell without causing complete destruction of a cell.
 
ii: Determine the impact of each nanomaterial type and dose on the expression of key marker genes in macrophages using doses where cells remain viable.
 
Our findings:
 
All nanomaterials tested were stimulatory to immune cells as measured through inflammatory gene expression (IL1) in trout macrophages. However, nanomaterials differed in the dose at which this gene expression began and the extent of stimulation. In addition, functionalization of these nanomaterials may increase this effect. This indicates that nanomaterials differ in their impact on the immune system and that functionalization can affect immune effects. There is a dose-response effect of nanomaterials on the immune response of trout macrophages with differences seen in the inflammatory responses to different nanomaterials at levels at or below 1 ug/mL, but each increased in response with increasing dose. The exception to this rule were the hydroxylated fullerenes, which appeared to have an inhibitory response to gene expression measures. This may have been due to actual suppression of cell response or suppression of the gene expression measurement.
 
iii. For selected nanomaterials that stimulate key marker genes, characterize global gene expression patterns using a custom microarray.
 
A microarray specifically designed to probe the global immune response of macrophages was used to examine differences in gene expression across nanomaterial treatments and to compare these expression patterns to traditional immune stimulants from viruses and bacteria. Even though each nanomaterial caused a similar inflammatory response in macrophage cells at 5 ug/ml exposures, the global gene expression differed with functionalization of nanomaterial. This was mainly in the form of the types of genes expressed in each nanomaterial treatment indicating a fundamental difference in response to each nanomaterial rather than just a generalized anti-inflammatory response.

 

Conclusions:

Our results indicate that fullerenes as well as single wall nanotubes and multiwall nanotubes are stimulatory to primary immune cells and they exhibit a dose-response effect and the immune cells react to each differently. Functionalization of nanomaterial may have an even greater impact on response than the core structure of the nanomaterial.
 
Side-chains used on NPs may have significant effects on their own. For example, cyclodextrin is a stimulator of inflammatory gene expression in trout macrophages. Surfactants used to solubilize NPs may have significant effects on gene expression. Deoxycholate and tetrahydrofuran are both stimulatory of inflammatory gene expression in trout macrophages.
 
Because we found a significant impact of surfactants on stimulation of our cell culture system, we moved completely away from using these suspensions and instead stirred our particles into suspension without the surfactant present with the understanding that this creates a slight alteration of the external aggregation. Of course, the functionalized nanoparticles were created to increase solubility and negate the need for the surfactant in the first place. Because of these properties, they are particularly attractive for industries and therefore more relevant exposures.
 
We determined that immune cell viability was not impacted by nanomaterial exposures up to 10 µg/mL concentrations. However, surfactants as well as chemicals used for functionalization impact cell viability slightly can can cause an inflammatory reeation that can be equal to that of the nanomaterials themselves. We have found that despite a lack of change in cell viability, nanomaterials vary in their stimulation of the immune response such as IL1. All nanomaterials we have tested cause an increase in candidate proinflammatory genes that is equivalent to stimulation of positive controls at the highest concentration of 10µg/mL but as the concentration drops to 1 or .1 µg/mL, there are differences in inflammatory responses with nanomaterials with differing chemistries and in a dose dependent fashion. There are a couple of nanomaterials that appear to be immune suppressive at all exposures tested. This would indicate that the dose that ultimately enters the organism will be extremely important to determine potential immune responses.

We have found that, despite a lack of change in cell viability, nanomaterials vary in their stimulation of the immune response as indicated by QPCR of genes indicative of an inflammatory response such as IL1. All nanomaterials we have tested cause an increase in candidate proinflammatory genes that is equivalent to stimulation of positive controls at the highest concentration of 10 ug/mL, but as the concentration drops to 1or .1 ug/mL, there are differences in inflammatory responses with nanomaterials with differing chemistries and in a dose dependent fashion. There are a couple of nanomaterials that appear to be immune suppressive at all exposures tested. This would indicate that the dose that ultimately enters the organism will be extremely important to determine potential immune responses.

A microarray specifically designed to probe the global immune response of macrophages was used to examine differences in gene expression across nanomaterial treatments and to compare these expression patterns to traditional immune stimulants from viruses and bacteria. Even though each nanomaterial caused a similar inflammatory response in macrophage cells at 5 ug/mL exposures, the global gene expression differed with functionalization of nanomaterial and with core structure. This was mainly in the form of the types of genes expressed in each nanomaterial treatment indicating an overall difference in response to each nanomaterial.

 


Journal Articles on this Report : 1 Displayed | Download in RIS Format

Publications Views
Other project views: All 18 publications 1 publications in selected types All 1 journal articles
Publications
Type Citation Project Document Sources
Journal Article Klaper R, Arndt D, Setyowati K, Chen J, Goetz F. Functionalization impacts the effects of carbon nanotubes on the immune system of rainbow trout, Oncorhynchus mykiss. Aquatic Toxicology 2010;100(2):211-217. R833319 (2009)
R833319 (Final)
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  • Supplemental Keywords:

    Risk assessment, dose response, exposure, immunology, ecological effects, nanotoxicology, immunotoxicology, genomics, biomarkers, Health, Scientific Discipline, Health Risk Assessment, Risk Assessments, Environmental Chemistry, bioavailability, nanomaterials, manufactured nanomaterials, environmental risks, aquatic ecosystem, biological pathways, biogeochemistry, bioaccumulation, nanochemistry, nanotechnology, nanoparticle toxicity, cellular response to nanoparticles, toxicologic assessment

    Relevant Websites:

    University of Wisconson - Milwaukee School of Freshwater Sciences: Rebecca D. Klaper Exit

    Progress and Final Reports:

    Original Abstract
  • 2008 Progress Report
  • 2009 Progress Report
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    The perspectives, information and conclusions conveyed in research project abstracts, progress reports, final reports, journal abstracts and journal publications convey the viewpoints of the principal investigator and may not represent the views and policies of ORD and EPA. Conclusions drawn by the principal investigators have not been reviewed by the Agency.

    Project Research Results

    • 2010
    • 2009 Progress Report
    • 2008 Progress Report
    • Original Abstract
    18 publications for this project
    1 journal articles for this project

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