Adverse Health Effects Associated with the Indoor Air Quality of Flood-Damaged Structures

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Proactive By Design. Our Company Commitment Adverse Health Effects Associated with the Indoor Air Quality of Flood-Damaged Structures June 23, 2016 Kimberly A. Hoppe Parr, PhD. GZA GeoEnvironmental, Inc. Page 1

Understanding and Communicating the Health Effects Associated with Indoor Air Quality of Flood-Damaged Structures Health effects Components impacting Indoor Air Quality (IAQ) of flooddamaged buildings Associated adverse health effects Communication Public outreach Recommendations on re-entry Page 2

Potential Hazardous Materials Associated with Flood Waters and Damaged Building Materials Chemicals Businesses, industry, agriculture, storage tanks, and household Cars, trucks, and other motorized vehicles Sewage Debris Damaged Building Material Asbestos Lead Carbon monoxide Unventilated equipment used during remediation (e.g.generators) Bioaersols Page 3

Bioaerosols Flooding is known to negatively impact indoor air quality by providing a nutrient-rich and moist habitat for microbial organisms to flourish Microbial Contaminants Bacteria Endotoxin Fungi/ mold Fungal spores (13)-β-d-glucan mycotoxins Page 4

Bacteria Small, single-celled organisms without a nucleus; many required for life, while many are disease-causing Legionnaire s Disease: Legionella Anthrax: Bacillus anthracis Microbial Volatile Organic Compounds (mvocs) By-products of microbial metabolism Low odor thresholds Endotoxin Page 5

Bacterial Toxicity: Endotoxin Lipopolysaccharide Integral component of the Gram-negative bacteria cell wall Shed into the environment during the growth cycle and when the bacteria die A recognized bacterial trigger of innate immunity and a causal agent for a variety of environmental lung diseases Asthma Decreased lung function Chronic bronchitis Organic Dust Toxic Syndrome Page 6

Fungi/Mold Unicellular and multicellular eukaryotic organisms Many species identified as causing human infections and adverse health effects. Need oxygen, food and water to grow and amplify Components Life cycle: Fungal spores Structural components: (13)-β-d-glucan and chitin Metabolic and defenses: mycotoxins and mvocs Page 7

Fungi/Mold Require water and nutrient source to proliferate 1. Indoor Nutrient Source The growing mold lives off of what it landed on, digesting the materials Construction materials Wood Carpet Materials high in cellulose 2. Indoor Water Source: Flooding Humidifiers Damp basements Plumbing leaks Page 8

Aftermath of Hurricane Katrina Water level Image courtesy of P.S. Thorne Page 9

Mold General Toxicity Several mold species and their related components are pathogenic to humans Inflammatory and toxic responses 1. Allergic reactions Asthma Allergies 2. Irritation Upper Respiratory system Skin Mucous membranes 3. Infections Aspergillosis Pneumocystis pneumonia 4. Toxic responses Mycotoxicosis Page 10

Mold Mycotoxins Toxic Mold = Toxigenic or Known to Produce Mycotoxins Species Aspergillus flavous Penicillium crustosum Stachbotrys chartarum (atra) Mycotoxin Alfatoxin Penitrem A Satratoxins Species are associated with water-damaged and damp building materials. Page 11

Mold Mycotoxins and mvocs Mycotoxins» Associated with the potential manifestation of disease and the disease process» Allergen» Potent Cytotoxins Causes cell disruption Interferes with cell processes Fungal mvocs» Associated with headaches, nasal irritation, fatigue Page 12

Mold Aspergillus Produce the Mycotoxin Aflatoxin o Sinus and local infections o Carcinogenic o Causes Aspergillosis (lung disease) Aspergillus does not usually cause disease in healthy individuals Infection can be fatal in immuno-compromised individuals Page 13

Mold Penicillium Not commonly pathogenic in healthy individuals Can be pathogenic in immuno-compromised and sensitive populations Skin, lung and gut infections Often treatable with anti-fungal remedies Page 14

Mold Stachybotrys Black Mold: Stachybotrys chartarum (atra) Indoor levels are usually low Frequently grow in flood-damaged building Favors building materials with high cellulose and low nitrogen content Reactions can include allergic rhinitis skin irritation sinus infection pink eye fatigue Photo: https://www.epa.gov/mold/mold-remediation-schools-and-commercial-buildings-guide Page 15

Mold Spores Spores (2-10 um) Part of the fungal life cycle Protective cases Mold can survive in a dormant spore state during harsh conditions Allow the mold to spread and distribute Associated health effects Allergies Upper respiratory tract irritant Figure: www.blackmould.me.uk/stachybotrys Page 16

Mold Glucan Fungi have rigid cell walls composed of chitin and glucans (polysaccharides) (13)β-D-glucans Exposure to (13)β-D-glucans can result in airway inflammation and an allergic response Mold does not have to be alive to trigger an immune response Page 17

Mold Pathology Etiology variable Toxicity influenced significantly by individual susceptibility Latency variable acute and chronic effects Multiple routes of exposure Page 18

Mold Pathology No standards or regulations PEL concept Dose response difficult to establish: Exposure = Dosage (Dose = Concentration x Time) Large variability in individual susceptibility Acute v. Chronic Toxicity Other Page 19

Mold Conclusions Mold is ubiquitous Many are toxic and are associated with adverse health effects Water intrusion is controlling factor No definitive regulations Page 20

Evaluating IAQ in Flood-Damaged Structures Visual Inspection Moisture levels on building materials Relative humidity indoors EPA recommends indoor humidity levels to be between 30-60% Occupant interviews Air Sampling Page 21

Why Evaluate IAQ after Flood? Overview Bacteria and mold grow optimally when moisture is present Flood and storm waters entering indoor environment Elevated indoor relative humidity HVAC system down, damaged building envelope, etc. Require a nutrient source Molds feed off dirt and debris left behind Water logged, decaying, carbon material can be a prime habitat for mold High concentrations of bioaerosols have been detected inside flood-damaged homes (Chew 2006, Rao 2007, Fabian 2005, Hoppe 2012) Page 22

IAQ: Bioaerosols in Flood-Damaged Structures Parameter Hoppe et al. Cedar Rapids In-progress Complete Chew et al. New Orleans Rao et al. New Orleans Nonflooded IAQ Culturable Bacteria (CFU/m 3 ) 1300 790 Culturable Mold (CFU/m 3 ) 420 180 22,000-515,000 32,700 88 2 Fungal Spores (spores/m 3 ) 540 480 82,000-630,000 280,000 211 2 ipm (µg/m 3 ) 78 34 52.9 1 i Endotoxin (EU/m 3 ) 1.55 0.3 17-139 23.3 0.64 1 i Glucan-linear (µg/m 3 ) 0.0256 0.007 0.0037 i Glucan-branched (µg/m 3 ) 0.0135 0.0034 1.6 1 Park et al. 2000: Massachusetts 2 Lee et al. 2000: Cincinnati Page 23

Why Evaluate IAQ after Flood? Health Effects Can trigger and create respiratory symptoms (Douwes 2003, Green 2006, Kurup 2000, Thorne 2000, Thorne 2006, Thorne & Duchaine 2007, Hoppe 2012, Rando 2013) Inflammatory response Asthma Allergies Develop hypersensitivities Organic Dust Toxic Syndrome (Schenker 1998) Flu-like symptoms: malaise, headache, cough, nauseas Firefighters after Hurricane Katrina- increased rate of developing new-onset upper respiratory symptoms sinus congestion, cough, and throat irritation (Tak 2007) Eye irritants Skin irritants Page 24

Communication & Public Outreach Factors contributing to increased bioaerosols Duration of flood water inundation High humidity- buildings cannot dry out Immediacy of home owners returning and performing muck and gut Page 25

Communication & Public Outreach Who should/ should not enter flood-damaged buildings? Is the building structurally sound? Page 26

Communication and Public Outreach What personal protective equipment (PPE) should be worn? CDC Page 27

Communication & Public Outreach Is cleaning effective? o o o Rapid and proper remediation is necessary to stop further mold growth Mold growth can begin within 48 hours (Johanning et al. 2014) Hoppe et al. 2012 in Cedar Rapids, Iowa Homes that had Completed renovation had significantly lower concentrations of indoor bioaerosols than homes that were still under-going renovation Study by He et al. 2014 in Brisbane, Australia This study provides quantitative evidence of the significant impact of immediate post-flood cleaning on mitigating the effects of flooding on indoor bioaerosol contamination and other pollutants. Yes, if done properly. Page 28

Practical Implications Water damaged building structures are associated with adverse health effects The number and severity of floods is on the rise and evidencebased recommendations are needed Proper remediation of flood-damaged homes can reduce bioaerosols to acceptable levels Exposures are significantly increased while remediation is inprogress leading to an increased burden of allergy and allergic rhinitis. Proper PPE should be worn during renovation Susceptible individuals are advised to not perform remediation Page 29

Thank you! Kimberly A. Hoppe Parr, PhD. Assistant Project Manager, Toxicologist GZA GeoEnvironmental, Inc. 20900 Swenson Dr. Waukesha, WI 53186 (262)754-2584 kimberly.parr@gza.com Page 30

References 1. CDC. Mold After a Disaster. October 7, 2015 available at: http://emergency.cdc.gov/disasters/mold/ 2. Hoppe, KA, et al. 2012. Assessment of Airborne Exposures and Health in Flooded Homes Undergoing Renovation. Indoor Air. 22(6):446-456. 3. Chew, GL et al. 2006. Mold and endotoxin levels in the aftermath of Hurricane Katrina: a pilot project of homes in New Orleans undergoing renovation. Environmental Health Perspective. 114:1883-1889. 4. Rao, CY, et al. 2007. Characterization of airborne molds, endotoxins, and glucans in home sin New Orleans after Hurricanes Katrina and Rite. Applied Environmental Microbiology. 73:1630-1634. 5. Tak S, et al. 2007. Floodwater exposure and the related health symptoms among firefighters in New Orleans, Louisiana. American Journal of Medicine. 50:277-382. 6. He, C., et al. 2014. The impact of flood and post-flood cleaning on airborne microbiological and particle contamination in residential houses. 7. Hasegawa et al. 2015. Indoor environmental problems and health status in waterdamaged homes due to tsunami disaster in Japan. Building and Environment. 93(1):24-34. 8. Johanning, E, et al. 2014. Review of health hazards and prevention measures for response and recovery workers and volunteers after natural disasters, flooding and water damage. Environmental Health Preventative Medicine. 19:93-99. Page 31