Laboratory and Field Evaluation of a New Methodology for the Sampling and Analysis of Fungal Fragments

Similar documents
Premise Microbial Testing

APPENDIX 13.2 A. Immunoassay. Fluorescent immunoassay. Enzyme immunoassay (ELISA) Radio immunoassay (RAST)

This article appeared in a journal published by Elsevier. The attached copy is furnished to the author for internal non-commercial research and

Analytical Service Code

β-n-acetylhexosaminidase (NAHA) as a Marker of Fungal Cell Biomass Storage Stability and Relation to β-glucan

NCCEH Mould Investigation Toolkit

INTRODUCTION: METHODOLOGY: November 4, Mr. Tom Heinz 353 West Sawgrass Dakota Dunes, SD 57049

The attached report is the result of a mold and bacterial assessment conducted at th Street, Franklin, Ohio on April 24 and 25, 2008.

AIR AND SURFACE SAMPLING MEASUREMENTS OF FUNGAL CONTAMINANTS IN INDOOR ENVIRONMENTS

INTRODUCTION: METHODOLOGY: November 11, Mr. Tim Squier 487 Deerfield Dakota Dunes, SD 57049

Field Performance of Portable Impactors when Enumerating Viable Bioaerosols

UNIVERSITY OF CINCINNATI

Sampling for Mould in Red Bluff Elementary School, Quesnel

ANALYSIS OF FUNGI (MOLD) IN THE INDOOR ENVIRONMENTS BY DIRECT MICROSCOPIC EXAMINATION. (Analysis Code: FDE)

AIRBORNE PARTICULATE MATTER WITHIN 100 RANDOMLY SELECTED OFFICE BUILDINGS IN THE UNITED STATES (BASE)

Healthy Buildings 2017 Europe July 2-5, 2017, Lublin, Poland. Evaluation of Risk of Mold Damages Based on a Novel Dust Sampling Method

IN THIS SECTION MICROBIOLOGY TESTING EXPERT SOLUTIONS FOR PRODUCT DEVELOPMENT. Bacterial Endotoxin (LAL) Testing

MVOC EMISSIONS FROM FUNGI IN HVAC SYSTEM

COMPARISON OF BIOCONTAMINANT LEVELS IN SCHOOLS -THE IMPACT OF CARPET VS. SMOOTH FLOOR COVERING

RESIDENTIAL MOLD ASSESSMENT. Final Report. Your Address Here

Post Remediation Testing Site Evaluation with Environmental Sampling

BIOAIRE CASSETTE Impaction Particle Sampler

Dalrymple Consulting, Inc. "Your Environmental Engineering Source" 7841 SW 1 i b Street, Topeka, Kansas (785) FAX (785)

NCCEH Mould Investigation Toolkit

DRAFT. UNR Fungi Assessment & Remediation Program

Table 1: Fungal Particulate Air Sample Results. ST-32 Room 17; post clean-up 5. 2 nd floor; commons area adjacent to Room 617

Rowan University Department of Environmental Health and Safety. A Brief Overview for Building Maintenance

Professional remediation of the school began on the weekend of October 5, 2013 and is due to continue until the entire building can be remediated.

SPORE TRAP SAMPLING REPORT FOR CENTENNIAL LANE ELEMENTARY SCHOOL 3825 CENTENNIAL LANE ELLICOTT CITY, MARYLAND PREPARED FOR:

SPORE SAMPLING REPORT FOR GLENWOOD MIDDLE SCHOOL 2680 ROUTE 97 GLENWOOD, MD PREPARED FOR:

SPORE SAMPLING REPORT FOR GLENWOOD MIDDLE SCHOOL 2680 ROUTE 97 GLENWOOD, MD PREPARED FOR:

MOLD REMEDIATION PROCEDURES AT A NEW JERSEY ELEMENTARY SCHOOL

Post Remediation Testing Site Evaluation with Environmental Sampling

Re: Elizabeth Middle School at County Road 13 in Elizabeth, CO Limited Ambient Microflora Inspection & Sampling

Premise Microbial Testing

Indoor Air Quality Report

Levels of Gram-Negative Bacteria, Aspergillus fumigatus, Dust, and Endotoxin at Compost Plants

ASSESSMENT OF BIOAEROSOL DISTRIBUTIONS IN MUNICIPAL SOLID WASTE TRANSFER STATION

Molecular Entrapment to Capture Airborne Mold Spores

Indoor and Outdoor Comparisons of Particle Sizes and Concentrations

Basic Industrial Hygiene Sampling Overview of Indoor Air Quality

Aalborg Universitet. CLIMA proceedings of the 12th REHVA World Congress Heiselberg, Per Kvols. Publication date: 2016

Health & Public Safety Management

TN Tatem Middle School Indoor Air Quality Assessment September 2016

Assessing Exposures to Compost Workers from Airborne BioHazards

A Study of Indoor Environmental Quality Parameters in a South Central Kentucky Daycare Facility

Effects of Sampling Time and Data Interpretation Methods on The Quality of Airborne Data

ISO INTERNATIONAL STANDARD. Indoor air Part 16: Detection and enumeration of moulds Sampling by filtration

THE BI-AIR FILTER CASSETTE: SAMPLING AIRBORNE FUNGAL SPORES IN A SETTLING CHAMBER. Joe Spurgeon, Ph.D., CIH Indoor Health Associates

THE EFFECT OF DUCT CLEANING ON INDOOR AIR QUALITY IN OFFICE BUILDINGS

S outhwest GEOSCIENCE. Analytical Results/Chain of Custody

CHARACTERIZATION OF INDUSTRIAL FILTRATION SYSTEMS FOR FINE PARTICLE

SPORE SAMPLING REPORT FOR GLENWOOD MIDDLE SCHOOL 2680 ROUTE 97 GLENWOOD, MD PREPARED FOR:

A MICROBIAL RESISTANCE EVALUATION OF INDOOR MATERIALS AIR KRETE INSULATION SAMPLE. prepared for AIR KRETE

USE OF IN-DUCT UVC LAMPS TO INACTIVATE AIRBORNE ENVIRONMENTAL BACTERIA AND FUNGI

INDOOR AIR QUALITY ASSESSMENT

Fungal Resistance of Calcium Silicate Boards

HOMEWORK WITH THE PAIR

MICROBIO BIOAEROSOL SAMPLING

Air Sampling for Manganese

Quantitative Analysis of Microbial Aerosols in a Community College Beta Theta Omicron Chapter of Phi Theta Kappa * Skyline College, San Bruno CA

Development of Experimental Procedure to Evaluate Potential Movement of Mold Spores from Wall Cavity to Indoor Environment

Critical control points for the management of microbial growth in HVAC systems

INTERPRETING MICROBIAL MEASUREMENT AND ANALYSIS

MARTIN AND WILLIAMSON HALL BUILDINGs Eastern Washington University, Cheney, Washington INDOOR AIR QUALITY SAMPLING PLAN

Rowan University New Jersey Public Employees Occupational Safety and Health Training

Spatial and temporal modelling of bioaerosols from intensive agricultural facilities in England

New Approach for the Efficient Collection of Airborne Particles down to 6 nm for Chemical and Toxicological Characterization

MOLD SCREENING REPORT

A highly sensitive assay for endotoxin detection and quantitation for a variety of sample types

A FIELD COMPARISON OF METHODS FOR ENUMERATING AIRBORNE FUNGAL BIOAEROSOLS

April 4, AHERA / Environmental Inspector Environmental Safety Office Old Marlboro Pike Upper Marlboro, MD 20772

Re cap of Events: February 8, Dear St. James Elementary Parents,

BIOAEROSOLS IN THE SUBURBS OF OSTRAVA DURING A ONE YEAR PERIOD

Influence of Algae Treatment on Lagoon Odors

Prabjit Barn Santé et environment: enjeux, rôles et interventions June 3, 2010 Montreal, QC

Birmingham 2080 Valleydale Road Suite 16 Birmingham, AL f: t:

No dry drains/traps were found, eliminating a potentially concern for odors.

FILTER EFFICIENCY OF SELECTED HVAC FILTERS

DATE: October 5, TO: Shawn Barr, Director. SUBJECT: Facility Services - IAQ - Air Test results - Jason Hughes' Office

Catalog Number: N190. Certificate of Analysis at

DATE: March 21, TO: Martha Gooding, Principal. SUBJECT: Ethridge ES - IAQ - Initial contact - Room A-5

Bacteria Aerosol Measurements Using Ventilation Filters in Building Air Handling Units

Occupational bioaerosol exposure in composting plants

DATE: October 21, TO: Susan Blockley, Director

A Comparison of U.S. Home Builder and New-home Homeowner Perceptions and Concerns about Mold

Report of Limited Indoor Air Quality Services

DATE: September 29, TO: Michael Wetchensky, Assistant Principal. SUBJECT: Rockbrook ES - IAQ - Initial Contact - Room 511

A L A R A Environmental Health & Safety Ltd.

OPERATING MANUAL. Model 900

FILED: NEW YORK COUNTY CLERK 07/14/ :42 PM INDEX NO /2016 NYSCEF DOC. NO. 25 RECEIVED NYSCEF: 07/14/2016

Technical Manual No Version

Birmingham 2080 Valleydale Road Suite 16 Birmingham, AL f: t:

Effects of fungal species, cultivation time, growth substrate, and air exposure velocity on the fluorescence properties of airborne fungal spores

PLEASE SCROLL DOWN FOR ARTICLE

December 28, Lewisville Independent School District 340 Lake Haven Lewisville, Texas Attn: Mr. Paul Siddall

DATE: February 28, TO: Robin Fry, Principal. SUBJECT: Polser ES - IAQ - Air Test - Room 200, 210 & Hallway outside 210

Airborne Mould Spore Assessment and Inspections

Transcription:

Laboratory and Field Evaluation of a New Methodology for the Sampling and Analysis of Fungal Fragments June 6, 2007 S. Seo 1, T. Reponen 1, F. Grimsley 2,T. Lee 1, C. Crawford 1, Y. Iossifova 1, D. Schmechel 3, C. Rao 4, S. Grinshpun 1. 1 Center for Health-Related Aerosol Studies, University of Cincinnati, Cincinnati, OH. 2 Tulane School of Public Health, New Orleans, LA. 3 National Institute for Occupational Safety and Health, Morgantown, WV. 4 Centers for Disease Control and Prevention, Atlanta, GA.

Background Indoor exposures to molds contribute to occupant respiratory disease and symptoms (IOM, 2004). However, previous studies have not been able to establish a clear cause-and and-effect relationship between inhalation of fungal particles and adverse respiratory effects. - No significant association between dampness or visible mold and the spore concentration level (Garrett et al., 1998; Chew et al., 2003). -1-

Background Exposures to submicrometer-sized sized fungal particles (i.e., fungal fragments) potentially contribute to adverse health effects due to: their (i) small physical size; (ii) composition - fungal antigens (Górny et al., 2002) and mycotoxins (Brasel et al., 2005). The contribution of these fungal fragments to exposure and adverse health outcomes are poorly characterized. -2-

Background (cont d) Assessing exposures to these fungal fragments for health effect studies is challenging due to: - Lack of a proper sampling method; The difficulty in collecting (the particle bounce problem) - Lack of the proper analyses: Traditional analytic methods such as culture-based method and microscopic method may not be suitable for analysis of submicron fungal particles. -3-

Background (cont d) (1-3) 3)-β-D-glucan has been used as a biomarker of fungal biomass (Chew et al., 2001; Rao et al., 2004). glycoprotein β-glucan Cell wall chitin membrane *Source: http://www.doctorfungus.org/thedrugs/images/glucan_target.jpg Beta-glucan and chitin : shape and rigidity of the cell wall structure. (1-3) 3)-β-D linkage is mainly related to fungi. (1-3) 3)-β-D-glucan : up to 60% of the dry weight of the cell wall of fungi (Douwes 2005). -4-

Objectives To develop and test a new sampling system for colleting submicrometer-sized sized fungal particles: To determine the feasibility of (1-3) 3)-β-D-glucan assay for quantifying submicrometer-sized sized fungal particles. To collect pilot data in moldy houses. -5-

To develop and optimize the new sampling system. To determine the feasibility of (1-3) 3)-β-D-glucan assay. -6-

Methods and Materials Experimental set-up Aerosolized Fungal particles Pump Filter OPC-1 12,345 OPC-1 CNC 100 > 2.5 um PM 2.5 PM 1.0 OPC-2 1,234 1.0-2.5 um -7-

Methods and Materials (cont d) Testing and optimization Penetration test: monodisperse PSL particles (0.54, 1.79, and 3.94 μm). Penetration rate (%) = N N downstream upstream 100 Bounce test with fungi - Microorganisms: Aspergillus versicolor and Stachybotrys chartarum. - Growth media: 1-week malt extract agar (MEA). -8-

Methods and Materials Feasibility test of (1-3) 3)-β-D-glucan assay (1-3) 3)-β-D-glucan assay: The kinetic chromogenic Limulus Amebocyte Lysate (LAL( LAL) ) assay. Procedure (i) Sample collection; (ii) Sample extraction; (iii) Take an aliquot (0.5 ml) (iv) LAL assay. air 0.05% Tween 2 ml An 0.5 ml aliquot Preloaded filter Cassette (After 1 hr) 2-min Vortexing 10-min Ultrasonic agitation -9-

Results Penetration curves and the D 50 values 100 PM2.5 Cyclone PM1.0 Cyclone Penetration rate (%) 50 Alternaria (11.2-17.8) Cladosporium (5.2-10.9) Starchybotrys (5.0-7.0) Ascospores (3.7-7.5) Aspergillus/ Penicillium (2.6-4.8) 0 1.05 2.25 1.0 2.0 3.0 4.0 5.0 Optical Diameter (µm) -10-

Results (cont d) Experiments on spore bounce Total spores collected onto after-filter as estimated by microscope (spores) 10 4 10 3 10 2 S. chartarum A. versicolor 10 1 10 6 10 7 10 8 10 9 Detection Limit (55) Total particle numbers entering the collection system as measured by the OPC-1 (particles) -11-

Results (cont d) Airborne (1-3) 3)-β-D-glucan concentration of fragment and spore size fractions (1-3)-β-D-glucan concentration (ng/m air 3 ) 10 4 10 3 10 2 10 1 10 0 Fragments Spores A. versicolor S. chartarum -12-

New Orleans (3 homes) and Southern Ohio (2 homes). Sampling seasons - Summer (June ~ September 2006). - Winter (Dec. 2006 ~ January 2007). -13-

Methods and Materials Sampling and measuring the (1-3) 3)-β-D-glucan - Button sampling (FIG. 1) and sampling of fragment sized particles (FIG. 2). - LAL assay. Particles Pump OPC PM 2.5 PM 1.0 FIG. 1. Button Inhalable sampler FIG. 2. Sampling box for fragment sized particles -14-

Methods and Materials (cont d) Photos (A) Installed in indoor (B) Installed in outdoor Picture 1. Field experimental Sep-up installed in: (A) indoor; and (B) outdoor air -15-

Methods and Materials (cont d) Picture 2. Moldy homes in New Orleans. -16-

Results The Fragment Collection System (FCS) vs. the Button Sampler 10 5 (1-3) 3)-β-D-glucan measured by the FCS (pg/m 3 ) 10 4 10 3 R = 0.919 (P<0.0001) 10 2 10 3 10 4 10 5 (1-3) 3)-β-D-glucan measured by the Button Sampler (pg/m 3 ) -17-

Results (cont d) Airborne (1-3) 3)-β-D-glucan Concentrations in Field Samples (1-3)-β-D-glucan concentrations (pg/m 3 ) 10 5 10 4 10 3 10 2 10 1 Summ er, n=15 Winter, n=6 Fragment Spore 10 0 Summer Winter -18-

Results (cont d) Fragment/spore Ratio in Field Samples 2.00 Field test 1.00 F/S ratio Laboratory test 0.00-1.00 A. versicolor S. chartarum Summer Winter -19-

Conclusions Laboratory evaluation showed that fungal fragments can be successfully separated from intact spores. The (1-3) 3)-β-D-glucan assay proved to be sensitive enough for the analysis of all tested fungal aerosols including submicron fungal fragments in size-fractioned samples. The good agreement between the measurements of the Button and FCS shows the capability of the Fragment Collection System combined with (1-3) 3)-β-D-glucan assay for quantifying fungal particles in fragment and spore size fraction in real field conditions. -20-

Conclusions The results of field sampling showed that the fragment size fraction contained considerable amount of (1-3) 3)-β-D-glucan,, which was comparable to the amount measured in the spore size fraction in many situations. This is inhalable size-selective selective sampling method. The new methodology is a promising tool for collection and analysis of fragments. -21-

Conclusions Laboratory evaluation showed that fungal fragments can be successfully separated from intact spores. The (1-3) 3)-β-D-glucan assay proved to be sensitive enough for the analysis of all tested fungal aerosols including submicron fungal fragments in size-fractioned samples. The good agreement between the measurements of the Button and FCS S shows the capability of the Fragment Collection System combined with (1-3) 3)-β-D-glucan assay for quantifying fungal particles in fragment and spore size fraction in real field conditions. The results of field sampling showed that the fragment size fraction contained considerable amount of (1-3) 3)-β-D-glucan,, which was comparable to the amount measured in the spore size fraction in many situations. The new methodology is a promising tool for collection and analysis of fragments. This is inhalable size-selective selective sampling method. -22-

Acknowledgment This research was supported by the National Institute for Occupational Safety and Health (Contract No. Q116-040 040-N819-1904) 1904) to the University of Cincinnati. Funded by the National Institute of Environmental Health Sciences (NIEHS) Center for Environmental Genetics Pilot Project Program (grant #PO30ES006096). Funded by the National Institute of Occupational Safety and Health NORA Research Program of the University of Cincinnati Education and Research Center (#T42/CCT510420). -23-

-24-

Research Design and Methods Specific Aim 2. Biological assay: β-glucan assay. Cascade of LAL Assay. Sample (β-glucan) Activated Factor G + Inactive clotting Enzyme Activation Active Clotting Enzyme Amebocyte Coagulogen (Substrate) Detecting Coagulin (Clot) -25-