Asthma prevalence trends by weight status among US children aged 2-19 years, 1988-2014.

BACKGROUND: Obesity is a risk factor for asthma. However, it is unclear if increased obesity prevalence contributed to rising childhood asthma prevalence. OBJECTIVE: To assess if population-level changes in weight status impacted asthma prevalence over time. METHODS: Using nationally representative 1988-2014 National Health and Nutrition Examination Survey data for 40 644 children aged 2-19 years, we analyzed asthma trends by weight status (body mass index age-specific percentiles determined using measured weight and height). Logistic regression and population attributable fraction were used to assess the association between obesity and asthma prevalence. RESULTS: Although obesity was a risk factor for asthma throughout the period, asthma prevalence increased only among children with normal weight; there was no interaction between weight status and time. The population attributable fraction for overweight/obesity rose from 8.5% in 1988-1994 to 11.9% in 2011-2014, but this increase was not significant (P = 0.44). CONCLUSIONS: Together, these data do not support a contribution of obesity trends to asthma prevalence trends.

Anthropometric Reference Data for Children and Adults: United States, 2011-2014.

Anthropometry or human body measurements provide important indicators of nutritional status in children and adults (1). In children, measurements reflect general health status, dietary adequacy, and growth and development over time. In adults, body measurements are used to evaluate health and dietary status, disease risk, and body composition. This report presents anthropometric reference data for 2011-2014 for U.S. children and adults.

Overview and quality assurance for the National Health and Nutrition Examination Survey (NHANES) oral health component, 1999-2002.

The Oral Health Component of the 1999-2002 National Health and Nutrition Examination Survey (NHANES) is a collaborative effort between the National Institute of Dental and Craniofacial Research (NIDCR), the National Center for Chronic Disease Prevention and Health Promotion, Division of Oral Health (NCCDPHP/DOH), and the National Center for Health Statistics (NCHS). The current NHANES is designed as a continuous survey with data released on a 2-year cycle to represent the civilian, non-institutionalized population of the US. Oral health data are currently available for 8082 and 9010 persons aged > or =2 years who participated in the 1999-2000 and 2001-2002 NHANES, respectively. This article provides background information on previous national examination surveys with oral health content. It also provides general analytical considerations, oral health content information, and evaluations of data quality in terms of examiner reliability statistics (percent agreements, kappa, and correlation coefficients) for the 1999-2002 NHANES Oral Health Component.

Urinary mercury concentrations associated with dental restorations in adult women aged 16-49 years: United States, 1999-2000.

BACKGROUND: Mercury amalgam dental restorations have been used by dentists since the mid 19th century and issues on safety continue to be periodically debated within the scientific and public health communities. Previous studies have reported a positive association between urine mercury levels and the number of dental amalgams, but this relation has never been described in a nationally representative sample in the United States. AIMS AND METHODS: Using household interview, dietary interview, dental examination, and laboratory data from the 1999-2000 National Health and Nutrition Examination Survey (NHANES), the association between mercury concentrations and dental restorations was examined in US women of reproductive age. RESULTS: In women of childbearing age, approximately 13% of all posterior dental surfaces were restored with amalgams and the average urinary mercury level in women was low (1.34 microg/l). It is estimated that an increase of 1.8 microg/l in the log transformed values for mercury in urine would occur for each 10 dental surfaces restored with amalgam. CONCLUSIONS: Although the findings do not address the important issues of adverse health effects at low thresholds of mercury exposure, they do provide important reference data that should contribute significantly to the ongoing scientific and public health policy debate on the use of dental amalgams in the USA.

Mortality from non-malignant respiratory disease in the fibreglass manufacturing industry.

OBJECTIVES: To investigate the question of whether there is an association between workplace exposures and sociodemographic factors and mortality from non-malignant respiratory disease excluding influenza and pneumonia (NMRDxIP) among workers in a fibreglass wool manufacturing facility. METHODS: A case-control study with cases and controls derived from deaths recorded from the Kansas City plant in the Owens Corning mortality surveillance system. The cases are defined as decedents with NMRDxIP as the underlying cause of death. Matched, unadjusted odds ratios (ORs) were used to assess any association between NMRDxIP and cumulative exposure history and sociodemographic factors individually. Matched, adjusted ORs were obtained by conditional logistic regression to estimate the effect of any one variable while controlling for the effect of all the others. RESULTS: Results of the unadjusted analysis, considering variables one at a time, yielded no significant associations between NMRDxIP and any of the exposure or sociodemographic variables. The smoking OR was substantially increased (OR 5.09; 95%CI 0.65 to undeterimed). Also, there were no significant variables in a conditional logistic regression analysis in which all variables were simultaneously adjusted. ORs for respirable glass fibres were below unity at all concentrations of exposure in the adjusted analysis. For respirable silica there was no consistent relation across all exposure levels. The ORs increased through the first three exposure concentrations but decreased for the highest exposure. However, ORs although not significant, are greater than unity for all respirable concentrations of silica exposure. CONCLUSIONS: The findings for Kansas City show no association between respirable glass fibres and NMRDxIP. The adjusted ORs for all exposures to respirable fibres were less than unity. On the other hand, the ORs for silica exposures were all above unity although there was no clear dose-response relation and none of the ORs were significant. Exposures for all substances considered were very low. Further, given the number of cases and controls, the statistical power to detect relatively small increases in risk, if any increase truly exited, was relatively low. The ORs for exposures to silica were all above unity although there was no clear dose-response relation and none of the ORs were significant. These raised ORs for silica suggest that continued surveillance would be prudent.

An historical cohort mortality study of synthetic fiber workers potentially exposed to glycerol polyglycidyl ether.

We report an update of the mortality experience of a cohort of 8878 employees who worked between November 1, 1965, and December 31, 1988, at a synthetic fiber manufacturing facility with potential exposure to glycerol polyglycidyl ether (T55) and were followed through December 31, 1998. The mortality experience of the race/gender groups within the cohort was strikingly similar, with both the all causes of death and all cancer causes of death below unity on both national and local standards. For white men, there were no statistically significant increases for any cause of death, with the exception of benign neoplasms. Thirty-four percent of the cohort had worked at the plant for less than 1 year. Standardized mortality ratios were compiled for those with less than 1 year of employment and for those with 1 year or more of employment. Exclusion of those cohort members who worked less than 1 year had little impact on the standardized mortality ratios.

Mortality from nephritis and nephrosis in the fibreglass manufacturing industry.

OBJECTIVES: To investigate the question of whether there is an association between exposure to silica or respirable glass fibre and mortality from nephritis or nephrosis among workers in fibrous glass wool manufacturing facilities. METHODS: A case-control study with cases and controls derived from the Owens Corning mortality surveillance system. Two case-control analyses were carried out, one where the cases are defined with nephritis or nephrosis as the underlying cause of death and one where cases are defined as those where nephritis or nephrosis is either the underlying or a contributing cause of death. RESULTS: There is no consistent relation between respirable fibres or respirable silica and nephritis or nephrosis when the analysis is based either on underlying cause only or on underlying plus contributing cause of death. None of the sociodemographic variables considered suggests an increased risk when considering both underlying and contributing cause of death. CONCLUSIONS: These data would seem to support the contention that the most accurate picture of renal disease will be gained from the use of all information on the death certificate and not only the underlying cause. For these data, all odds ratios (ORs) for respirable fibres and silica based on both underlying and contributing cause of death are < 1 with the exception of the highest exposure to silica which is slightly > 1 (OR = 1.04). Although these results do not prove that there is no association between nephritis and nephrosis and exposure to fibreglass or silica in the fibreglass manufacturing environment, they do not support the assertion that such an association exists.

Historical cohort mortality study of a continuous filament fiberglass manufacturing plant. II. Women and minorities.

An historical cohort mortality study was undertaken at Owens Corning's continuous filament fiberglass manufacturing plant in Anderson, South Carolina. The cohort included 1074 white women, 130 black women, and 494 black men who worked for a minimum of one year from the opening of the plant in 1951 through December 31, 1991. This represents the largest single cohort of white women assembled to date in either a wool or continuous filament fiberglass manufacturing facility and represents the first study of a cohort of black men and women in the man-made vitreous fiber industry. Over 95% of the women and minorities included in this report held production positions in the plant. There were no significant excesses or deficits in mortality by cause, including cancer causes, among white women, with the exception of motor-vehicle accidents, when compared with national mortality. Among black men, standardized mortality ratios (SMRs) for heart disease are significantly below one, and SMRs for all cancers combined are below unity on both national and local standards. Lung cancer SMRs are below unity for both white women and black men.

Historical cohort mortality study of a continuous filament fiberglass manufacturing plant. I. White men.

An historical cohort mortality study of a continuous filament fiberglass manufacturing plant was undertaken to determine whether an elevated lung cancer risk would be observed on a cohort basis. A nested case-control study of white male lung cancer deaths was incorporated into the study design. An interview survey to obtain information on sociodemographic factors, including smoking, and an historical environmental reconstruction to identify elements in the plant environment to which workers might be exposed were included in the study design. Respirable glass (Beta) fibers were produced only from 1963 to 1968. The lung cancer odds ratio (OR) among those workers exposed to respirable glass fibers is below unity, as are ORs for exposure to asbestos, refractory ceramic fibers, respirable silica (except for the lowest exposure level), total chrome and arsenic. There is a suggestion of an increase with exposure among smokers only for exposure to formaldehyde, although the OR for the highest level is based on only one case and is not likely to be meaningful. None of these plant exposures suggests an increase in lung cancer risk for this population. Although the lung cancer standardized mortality ratios are slightly elevated, results of the case-control investigation confirm that neither respirable glass fibers nor any of the substances investigated as part of the plant environment are associated with an increase in lung cancer risk for this population.

Adjustment for the confounding effect of cigarette smoking in an historical cohort mortality study of workers in a fiberglass manufacturing facility.

In 1986 a statistically significant lung cancer SMR based on U.S. white male national mortality rates was reported for male fibrous glass workers for follow-up through 1982 of a cohort of U.S. man-made mineral fiber workers. The Newark, Ohio, plant of Owens-Corning, which comprised 38% of the fibrous glass workers in that cohort, also exhibited a statistically significant lung cancer standardized mortality ratio based on U.S. white male mortality rates. A case-control study of the Newark workers demonstrated that a history of cigarette smoking and not exposure to respirable glass is the most important factor in lung cancer risk for workers at the Newark plant. We provide an estimate of the extent of confounding by cigarette smoking for the Newark plant nationally based lung cancer standardized mortality ratio with data not previously available and which suggests that adjusting for the confounding effect of cigarette smoking could reduce the lung cancer standardized mortality ratio to a non-statistically significant level.

A case-control study of malignant and non-malignant respiratory disease among employees of a fiberglass manufacturing facility. II. Exposure assessment.

A case-control study of malignant and non-malignant respiratory disease among employees of the Owens-Corning Fiberglas Corporation's Newark, Ohio plant was undertaken. The aim was to determine the extent to which exposures to substances in the Newark plant environment, to non-workplace factors, or to a combination may play a part in the risk of mortality from respiratory disease among workers in this plant. A historical environmental reconstruction of the plant was undertaken to characterise the exposure profile for workers in this plant from its beginnings in 1934 to the end of 1987. The exposure profile provided estimates of cumulative exposure to respirable fibres, fine fibres, asbestos, talc, formaldehyde, silica, and asphalt fumes. Employment histories from Owens-Corning Fiberglas provided information on employment characteristics (duration of employment, year of hire, age at first hire) and an interview survey obtained information on demographic characteristics (birthdate, race, education, marital state, parent's ethnic background, and place of birth), lifetime residence, occupational and smoking histories, hobbies, and personal and family medical history. Matched, unadjusted odds ratios (ORs) were used to assess the association between lung cancer or non-malignant respiratory disease and the cumulative exposure history, demographic characteristics, and employment variables. Only the smoking variables and employment characteristics (year of hire and age at first hire) were statistically significant for lung cancer. For non-malignant respiratory disease, only the smoking variables were statistically significant in the univariate analysis. Of the variables entered into a conditional logistic regression model for lung cancer, only smoking (smoked for six months or more v never smoked: OR = 26.17, 95% confidence interval (95% CI) 3.316-206.5) and age at first hire (35 and over v less than 35: OR = 0.244, 95% CI 0.083-0.717) were statistically significant. There were, however, increased ORs for year of employment (first hired before 1945 v first hire after 1945: OR = 1.944, 95% CI 0.850-4.445), talc (cumulative exposure >1000 fibres/ml days v never exposed: OR = 1.355, 95% CI 0.407-5.515), and asphalt fumes (cumulative exposure >0.01 mg/m(3) days v never exposed: OR 1.131, 95% CI 0.468-2.730). For non-malignant respiratory disease, only the smoking variable was significant in the conditional logistic regression analysis (OR = 2.637, 95% CI 1.146-6.069). There were raised ORs for the higher cumulative exposure categories for respirable fibres, asbestos, silica, and asphalt fumes. For both silica and asphalt fumes, ORs were more than double the reference groups for all exposure categories. A limited number of subjects were exposed to fine fibres. The scarcity of cases and controls limits the extent to which analyses for fine fibre may be carried out. Within those limitations, among those who had worked with fine fibre, the unadjusted, unmatched OR for lung cancer was (1.0 (95% CI 0.229-4.373) and for non-malignant respiratory disease, the OR was 1.5 (95% CI 0.336-6.702). The unadjusted OR for lung cancer for exposure to fine fibre was consistent with that for all respirable fibre and does not suggest an association. For non-malignant respiratory disease, the unadjusted OR for fine fibre was opposite in direction from that for all respirable fibres. Within the limitations of the available data on fibre, there is o suggestion that exposure to fine fibre has resulted in an increase in risk of lung cancer. The increased OR for non-malignant respiratory disease is inconclusive. The results of this population, in this place and time, neither respirable fibres nor any of the substances investigated as part of the plant environment are statistically significant factors for lung cancer risk although there are increased ORs for exposure to talc and asphalt fumes. Smoking is the most important factors in risk for lung cancer in this population. The situation is less clear for non-malignant respiratory disease. Unlike lung cancer, non-malignant respiratory represents a constellation of outcomes and not a single well defined end point. Although smoking was the only statistically significant factor for non-malignant respiratory disease in this analysis, the ORs for respirable fibres, asbestos, silica, and asphalt fumes were greater than unity for the highest exposure categories. Although the raised ORs for these substances may represent the results of a random process, they may be suggestive of an increased risk and require further investigation.

A case-control study of malignant and non-malignant respiratory disease among employees of a fiberglass manufacturing facility.

A case-control study was conducted to determine the influence of non-workplace factors on risk of respiratory disease among workers at the Owens-Corning Fiberglas plant in Newark, Ohio. Cases and controls were drawn from a historical cohort mortality study conducted on behalf of the Thermal Insulation Manufacturers Association (TIMA) of workers employed at Newark for at least one year between 1 January 1940 and 31 December 1963 and followed up to the end of 1982. The TIMA study reported a statistically significant increase in respiratory cancer (compared with national death rates). Interviews were completed for 144 lung cancer cases and 299 matching controls and 102 non-malignant respiratory disease cases and 201 matching controls. Unadjusted odds ratios (ORs) were used to assess the association between lung cancer or non-malignant respiratory disease and birthplace, education, income, marital state, smoking with a duration of six months or more, age at which smoking first started, and duration of smoking. Only the smoking variables were statistically significant. For lung cancer, of the variables entered into a conditional logistic regression model, only the smoking OR of 23.4 (95% CI 3.2-172.9) was statistically significant. For non-malignant respiratory disease no variables entered into the final model were statistically significant. Results of the interview portion of our case-control study clearly indicate that smoking is the most important non-workplace factor for risk of lung cancer in this group of workers. Smoking does not seem to play as important a part, however, for non-malignant respiratory disease. Prevalence of cigarette smoking at the Newark plant was estimated for birth cohorts by calendar year. Corresponding data for the United States were compiled from national smoking surveys. Prevalence of cigarette smoking for Newark in 1955 appears to be sufficiently greater than the corresponding United States data in 1955 to suggest that some of the previously reported excess of lung cancer for Newark based on United States mortality may be accounted for by differences in the prevalence of cigarette smoking between white men in Newark and those in the United States as a whole.