In the spring of 1993, hantavirus pulmonary syndrome (HPS) "emerged" in the southwestern United States, where a multiagency investigation led to the rapid description of this new clinical entity and its etiology. Analysis of the first 100 US cases identified showed that the disease was distributed in 21 states, had gone unrecognized since at least 1959, and had a distinct spring-early summer seasonality. Of the infected persons, 54% were male; 63% were Caucasian, 35% were Native American, and 2% were African American. The average age of case-patients was 34.9 years, and 8 were children or adolescents aged < or = 16 years. The overall case-fatality rate was 52%. There was a 91% concordance among serologic, immunohistochemical, and molecular results. HPS in the United States is caused by at least three newly described pathogenic hantaviruses, each of which has a distinct rodent host, and cases of HPS have been recently recognized in Canada and South America. National surveillance of this sporadic disease remains essential for further defining the epidemiology and clinical spectrum.
In the 15 years following licensure of acyclovir, resistance to the drug remains low among immunocompetent patients. However, 5% of HIV-positive patients had resistant HSV-2 isolates. Continued surveillance is essential to monitor changes in acyclovir resistance and to characterize the clinical and public health importance of acyclovir-resistant HSV.
Objectives
To evaluate respiratory related mortality among underground coal miners after 37 years of follow-up.
Methods
Underlying cause of death for 9033 underground coal miners from 31 US mines enrolled between 1969 and 1971 was evaluated with life table analysis. Cox proportional hazards models were fitted to evaluate the exposure-response relationships between cumulative exposure to coal mine dust and respirable silica and mortality from pneumoconiosis, chronic obstructive pulmonary disease (COPD) and lung cancer.
Results
Excess mortality was observed for pneumoconiosis (SMR=79.70, 95% CI 72.1 to 87.67), COPD (SMR=1.11, 95% CI 0.99 to 1.24) and lung cancer (SMR=1.08; 95% CI 1.00 to 1.18). Coal mine dust exposure increased risk for mortality from pneumoconiosis and COPD. Mortality from COPD was significantly elevated among ever smokers and former smokers (HR=1.84, 95% CI 1.05 to 3.22; HRK=1.52, 95% CI 0.98 to 2.34, respectively) but not current smokers (HR=0.99, 95% CI 0.76 to 1.28). Respirable silica was positively associated with mortality from pneumoconiosis (HR=1.33, 95% CI 0.94 to 1.33) and COPD (HR=1.04, 95% CI 0.96 to 1.52) in models controlling for coal mine dust. We saw a significant relationship between coal mine dust exposure and lung cancer mortality (HR=1.70; 95% CI 1.02 to 2.83) but not with respirable silica (HR=1.05; 95% CI 0.90 to 1.23). In the most recent follow-up period (2000–2007) both exposures were positively associated with lung cancer mortality, coal mine dust significantly so.
Conclusions
Our findings support previous studies showing that exposure to coal mine dust and respirable silica leads to increased mortality from malignant and non-malignant respiratory diseases even in the absence of smoking.
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