Bennion et al. (2007) |
Karakalpakstan, Uzbekistan |
Questionnaire‐based assessment of household exposures and self‐reported respiratory health (asthma, allergic rhinitis, pneumonia) |
Dust deposition rates (PM10 and PM2.5) within 5 km of study populations |
Some evidence for an inverse relationship between FEV1 and dust exposure, but no significant relationship was found |
Highest rates of dust deposition occurred during the summer months and in the region closest to the original shoreline |
Unable to test difference between asthma and allergic rhinitis |
Cross‐sectional study does not allow for testing for children with wheezing |
No significant variation between PM10 and PM2.5 fractions |
Pulmonary function (FEV1) collected via portable spirometer |
Crighton et al. (2003) |
Karakalpakstan, Uzbekistan |
Questionnaire‐based assessment of perceived environment, social support networks, psychosocial health, and self‐rated somatic health (general) |
None |
High rates of poor self‐rated health |
None |
Lower‐than‐expected ratings of poor health and environmental may be due to mass out‐migration from the region, leaving behind individuals who were less oncerned about these issues |
Respondents were more likely to have poor self‐rated health if they were concerned about environmental problems and had an intermediate or higher education level |
Indoitu et al. (2015) |
Aral Sea region |
None |
Remote sensing observations (satellite imagery, ozone mapping spectrometry) to track frequency, size, and sources of dust storms andaerosol concentrations over the region |
None |
The Aral Sea dry lake bed has been a strong source of dust emissions since 2000 and has included the northern and southern desert areas as dust sources |
Absence of meteorological monitoring stations on the dried Aral Sea surface |
Dust storm frequency, composition, and structure have changed as a result of the Aral Sea desiccation process |
Dust emissions originating from the Aralkum desert are capable of traveling hundreds of kilometers |
Kaneko et al. (2003) |
Kazalinsk District, Kazakhstan and control area |
Questionnaire‐based assessment of overall health, gastrointestinal symptoms |
None |
Significantly higher prevalence of gastrointestinal symptoms, abnormal renal labs in children living in the Aral Sea region vs. control |
None |
Unknown specific cause for renal tubular dysfunction found in the study area |
Renal tubular cell injury as measured by urine sampling |
Kunii et al. (2010) |
Kazalinsk District, Kazakhstan and control area |
Questionnaire‐based assessment of household exposures and respiratory symptoms (pneumonia, chest infection, wheeze) |
None |
Significantly higher prevalence of wheeze and restrictive pulmonary dysfunction among subjects in the Aral Sea region compared to those living farther away |
None |
Confounding factors related to measurement bias during questionnaire administration and weather‐related variability in pulmonary function performance |
No significant difference for asthma or obstructive pulmonary dysfunction |
O'Hara et al. (2000) |
Eastern Turkmenistan |
None |
Airborne dust deposition rates (PM10) and physical/chemical composition |
None |
Dust deposition rates were higher in desert monitoring sites than those closer to the Aral Sea |
None noted |
At sites near irrigated areas, PM10 values were greater |
High levels of phosphalone (organophosphate) contamination were found across sites and were highest in irrigated areas despite the cessation of pesticide spraying |
Wiggs et al. (2003) |
Karakalpakstan, Uzbekistan |
Questionnaire‐based assessment of household exposures and respiratory symptoms (chronic cough, wheeze, asthma) |
Dust deposition rates (PM10) within 5 km of study populations |
Children living closer to the former shoreline had a lower prevalence of respiratory health problems compared to main agricultural and urban areas |
Summer months experienced conditions (i.e., temperature, precipitation, and wind patterns) that were conducive to increased sediment erosion and dust transport, especially in the northern portion of the study area |
Likelihood that dust is not the only environmental factor that may cause changes in human health |
Dust deposition data indicates multiple potential sources of dust |
Pulmonary function (FEV1) collected via electronic volume‐flow spirometer |
Monthly aggregate data may mask short‐term effects on health caused by single dust events |
During the dusty season, deposition rates of PM10 far exceeded US EPA standards |