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Hanford: workplace beryllium exposure risk assessment . Wint Su Wai and Thanh-Hien Ngo. Hanford. History. Hanford is the most contaminated nuclear site in the western hemisphere Established in 1943 as part of the Manhattan Project to develop nuclear weapons for WWII
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Hanford: workplace beryllium exposure risk assessment Wint Su Wai and Thanh-Hien Ngo
History • Hanford is the most contaminated nuclear site in the western hemisphere • Established in 1943 as part of the Manhattan Project to develop nuclear weapons for WWII • Home to the B reactor, the first full-scale plutonium production reactor in the world • Focus of the nation's largest environmental cleanup
Stakeholders • Hanford Tri-Party Agreement - USDOE, USEPA, ECY-WA • Hanford Advisory Board • Indian Nations Program • Hanford Natural Resource Trustee Council • Local Advocacy Groups -Columbia Riverkeeper, Heart of America Northwest, Hanford Watch, Hanford Challenge, Physicians for Social Responsibility • Nuclear Safety Division of the Oregon Office of Energy • Washington State Department of Health
Present Threats • Water Contamination • 450 billion gallons of contaminated waste have been dumped into unlined soil trenches • 53 million gallons of waste in 177 underground storage tanks , 60 have leaked; contamination of groundwater near Columbia River • Atmospheric Contamination
Who is at risk? • Workers • 1 million people living in the 42 cities or towns located below Hanford on the Columbia • Draw water from Columbia for municipal, commercial & industrial uses. • Tribal members (Yakima, Utmilla, Nez Perce) • hunting, fishing, social gathering
Beryllium • Grayish, lightweight but strong alkaline earth metal • Mining, refining, and in the manufacture of ceramics, electronic, and aerospace equipment. • Used at Hanford from 1960 until 1986 in the production of nuclear fuel rods
“When certain sensitive individuals are exposed to even minute amounts of inhaled beryllium, they are at considerable risk of becoming beryllium sensitized and contracting a potentially fatal granulomatous lung disease called chronic beryllium disease (CBD) and an increased risk of lung cancer... ...from a worker health and safety perspective based on the number of affected workers, beryllium currently rates as a greater hazard than radiation.” - The Hanford Advisory Board
Routes of Exposure • Inhalation (Direct) • airborne particles of beryllium metal, alloys, oxides, and ceramics • Ingestion (Indirect) • Hand-to-mouth • Dermal (Indirect) • ultrafine particles
Adverse Health Affects • Beryllium Sensitization (BeS) to clinically apparent pulmonary disease • Acute disease: inflammation of lungs • Chronic beryllium disease (CBD) or berylliosis • Dermal and carcinogenic effects • Group B1: probable human carcinogen (EPA) • Group 1: human carcinogen (IARC)
Takaro et al. study:Screening for Beryllium Sensitization among Former Hanford Workers Beryllium workers respondent to date, May 1998: • AGE: 21-86 years old • Average: 62 years old • SEX: • 108 males (87.1%) • 16 females (12.9%)
Precautionary Assessment Unsupportive of health and community
Exposure Issues Relatively medium risk of exposure
Hazard/Toxicity Extremely hazardous !
A Reconsideration of Acute Beryllium Disease Cummings et al. 2009
Non-occupational BerylliosisEisenbudet al. 1949 • Looked at chronic disease among residents near Beryllium production plant • 11 cases • 10 lived within 0.75 miles from plant • 1 case was 1.75 miles away, husband worked at plant for 3 months • Conclusion • 10-week test period, average concentration of beryllium at a distance of 0.25 mile ranged between 0.004 - 0.02 ug/m3 • concluded that lowest exposure that produced disease was greater than 0.01ug/m3and less than 0.1ug/m3
Machining Risk of Beryllium Disease and Sensitization With Median ExposuresBelow 2 ug/m3Kreiss, et al. 1996
RfC (Reference Concentration) (ug/m3) = NOAEL (ug/m3) / Uncertainty Factors RfC for EPA : 0.02 ug/m3 NOAEL from Eisenbudet al.: 0.01-0.1 ug/m3 NOAEL from EPA: 0.1 ug/m3 RfC for Eisenbud: 0.005 ug/m3 /800 = 0.00000625 ug/m3 RfC for EPA: 0.1 ug/m3/ 800 = 0.000125ug/m3
Conclusions • Maximum concentration of beryllium via inhalation should be 0.000125 ug/m3 to prevent adverse health affects from workplace exposure.(EPA=0.02 ug/m3) • OSHA occupational exposure limit for 8-hr workshift 2 ug/m3 is not protective. • Should use ACGIH: 0.5 ug/m3 • More stringent regulations and guidelines at state, national, and international level.
Risk Management • Monitoring ambient concentrations • More studies for workplace inhalation exposure • data for possible chemical transformation of Beryllium and its half-life in air • limited information on reproductive or developmental effects • More adequate exposure monitoring
Genetic Susceptibility Age, gender, nutrition, behavior Exposure concentration, duration, frequency Adverse Health Risk: CBD, Lung Cancer Dose Hazard Screening Wellness Program Surveillance Progression Subclinical Disease (BeS) Occupational health standard, PPE, Engineering and Administration control Repair Healthy Worker Pathways from exposure to disease showing modifying factors and opportunities for interventions.
Risk Communication • Promote awareness towards Beryllium exposure • Preventive Focused Education for workers : safety, PPE, changing clothes • AdvanceMed Hanford’s Beryllium Monitoring Program • BeLPT (Beryllium Lymphocyte proliferation test) • Chest radiographs • Pulmonary Function Tests • Carbon monoxide diffusion • Regular follow-up visits
Media Coverage • Do not always get it right • Loss of interest • Disaster or loss of funding newsworthy