Ellis Hugh, Schoenberger Erica
Department of Geography and Environmental Engineering, Johns Hopkins University, Baltimore Maryland, United States of America.
PLoS One. 2017 Jan 26;12(1):e0170451. doi: 10.1371/journal.pone.0170451. eCollection 2017.
According to the most recent estimates, 842,000 deaths in low- to middle-income countries were attributable to inadequate water, sanitation and hygiene in 2012. Despite billions of dollars and decades of effort, we still lack a sound understanding of which kinds of WASH interventions are most effective in improving public health outcomes, and an important corollary-whether the right things are being measured. The World Health Organization (WHO) has made a concerted effort to compile comprehensive data on drinking water quality and sanitation in the developing world. A recent 2014 report provides information on three phenotypes (responses): Unsafe Water Deaths, Unsafe Sanitation Deaths, Unsafe Hygiene Deaths; two grouped phenotypes: Unsafe Water and Sanitation Deaths and Unsafe Water, Sanitation and Hygiene Deaths; and six explanatory variables (predictors): Improved Sanitation, Unimproved Water Source, Piped Water To Premises, Other Improved Water Source, Filtered and Bottled Water in the Household and Handwashing.
Regression analyses were performed to identify statistically significant associations between these mortality responses and predictors. Good fitted-model performance required: (1) the use of population-normalized death fractions as opposed to number of deaths; (2) transformed response (logit or power); and (3) square-root predictor transformation. Given the complexity and heterogeneity of the relationships and countries being studied, these models exhibited remarkable performance and explained, for example, about 85% of the observed variance in population-normalized Unsafe Sanitation Death fraction, with a high F-statistic and highly statistically significant predictor p-values. Similar performance was found for all other responses, which was an unexpected result (the expected associations between responses and predictors-i.e., water-related with water-related, etc. did not occur). The set of statistically significant predictors remains the same across all responses. That is, Unsafe Water Source (UWS), Improved Sanitation (IS) and Filtered and Bottled Water in the Household (FBH) were the only statistically significant predictors whether the response was Unsafe Sanitation Death Fraction, Unsafe Hygiene Death Fraction or Unsafe Water Death Fraction. Moreover, the fraction of variance explained for all fitted models remained relatively high (adjusted R2 ranges from 0.7605 to 0.8533). We find that two of the statistically significant predictors-Improved Sanitation and Unimproved Water Sources-are particularly influential. We also find that some predictors (Piped Water to Premises, Other Improved Water Sources) have very little explanatory power for predicting mortality and one (Other Improved Water Sources) has a counterintuitive effect on response (Unsafe Sanitary Death Fraction increases with increases in OIWS) and one predictor (Hand Washing) to have essentially no explanatory usefulness.
Our results suggest that a higher priority may need to be given to improved sanitation than has been the case. Nevertheless, while our focus in this paper is mortality, morbidity is a staggering consequence of inadequate water, sanitation and hygiene, and lower impact on mortality may not mean a similarly low impact on morbidity. More specifically, those predictors that we found uninfluential for predicting mortality-related responses may indeed be important when morbidity is the response.
根据最新估计,2012年中低收入国家有84.2万人的死亡归因于水、环境卫生和个人卫生条件不足。尽管投入了数十亿美元并历经数十年努力,但我们仍未充分了解哪种水、环境卫生和个人卫生(WASH)干预措施在改善公众健康结果方面最为有效,以及一个重要的推论——所衡量的指标是否正确。世界卫生组织(WHO)已齐心协力汇编发展中世界饮用水质量和环境卫生的综合数据。2014年的一份近期报告提供了三种表型(反应)的信息:不安全饮用水导致的死亡、不安全环境卫生导致的死亡、不安全个人卫生导致的死亡;两种分组表型:不安全饮用水和环境卫生导致的死亡以及不安全饮用水、环境卫生和个人卫生导致的死亡;以及六个解释变量(预测因素):改善的环境卫生、未改善的水源、管道水接入住所、其他改善的水源、家庭中的过滤水和瓶装水以及洗手。
进行回归分析以确定这些死亡率反应与预测因素之间的统计学显著关联。良好的拟合模型性能要求:(1)使用人口标准化死亡比例而非死亡人数;(2)对反应进行变换(对数或幂变换);(3)对预测因素进行平方根变换。鉴于所研究关系和国家的复杂性与异质性,这些模型表现出显著性能,例如,解释了人口标准化不安全环境卫生死亡比例中约85%的观察方差,具有较高的F统计量和高度统计学显著的预测因素p值。所有其他反应也有类似表现,这是一个意外结果(反应与预测因素之间预期的关联,即与水相关的因素与水相关的因素等并未出现)。在所有反应中,具有统计学显著意义的预测因素集保持不变。也就是说,不安全水源(UWS)、改善的环境卫生(IS)以及家庭中的过滤水和瓶装水(FBH)是唯一具有统计学显著意义的预测因素,无论反应是不安全环境卫生死亡比例、不安全个人卫生死亡比例还是不安全饮用水死亡比例。此外,所有拟合模型解释的方差比例仍然相对较高(调整后的R²范围从0.7605到0.8533)。我们发现两个具有统计学显著意义的预测因素——改善的环境卫生和未改善的水源——特别有影响力。我们还发现一些预测因素(管道水接入住所、其他改善的水源)对预测死亡率的解释力很小,其中一个(其他改善的水源)对反应有违反直觉的影响(不安全卫生死亡比例随着其他改善水源的增加而增加),还有一个预测因素(洗手)基本上没有解释作用。
我们的结果表明,可能需要比以往更优先考虑改善环境卫生。然而,虽然我们在本文中的重点是死亡率,但发病率是水、环境卫生和个人卫生条件不足造成的惊人后果,对死亡率影响较小并不意味着对发病率的影响同样小。更具体地说,我们发现对预测与死亡率相关的反应没有影响力的那些预测因素,当反应是发病率时可能确实很重要。