Abstract
Sanitary risk inspection, an observation protocol for identifying contamination hazards around water sources, is promoted for managing rural water supply safety. However, it is unclear how far different observers consistently identify contamination hazards and consistently classify water source types using standard typologies. This study aimed to quantify inter-observer agreement in hazard identification and classification of rural water sources. Six observers separately visited 146 domestic water sources in Siaya County, Kenya, in wet and dry seasons. Each observer independently classified the source type and conducted a sanitary risk inspection using a standard protocol. Water source types assigned by an experienced observer were cross-tabulated against those of his colleagues, as were contamination hazards identified, and inter-observer agreement measures calculated. Agreement between hazards observed by the most experienced observer versus his colleagues was significant but low (intra-class correlation = 0.49), with inexperienced observers detecting fewer hazards. Inter-observer agreement in classifying water sources was strong (Cohen’s kappa = 0.84). However, some source types were frequently misclassified, such as sources adapted to cope with water insecurity (e.g. tanks drawing on both piped and rainwater). Observers with limited training and experience thus struggle to consistently identify hazards using existing protocols, suggesting observation protocols require revision and their implementation should be supported by comprehensive training. Findings also indicate that field survey teams struggle to differentiate some water source types based on a standard water source classification, particularly sources adapted to cope with water insecurity. These findings demonstrate uncertainties underpinning international monitoring and analyses of safe water access via household surveys.
Highlights
Target 6.1 of the Sustainable Development Goal (SDG) aims to ‘By 2030, achieve universal and equitable access to safe and affordable drinking water for all’ (United Nations 2019)
As well as being promoted as a tool for water supply managers, sanitary risk inspection has been used in national water source surveys, such as the Rapid Assessment of Drinking-Water Quality (RADWQ) survey series (World Health Organization and UNICEF 2012)
Building on preliminary work in Ghana, we have undertaken the first assessment of inter-observer agreement in water source classification and contamination hazard identification at such sources
Summary
Target 6.1 of the Sustainable Development Goal (SDG) aims to ‘By 2030, achieve universal and equitable access to safe and affordable drinking water for all’ (United Nations 2019) To deliver this target, the World Health Organization has promoted water safety plans as a tool for rural water supply managers to ensure the safety of such supplies (Rickert et al 2014). Where microbiological testing does take place, supply managers require methods for identifying the hazards responsible for the microbiological contamination identified through water testing so that these can be remediated For this reason, the World Health Organization (WHO) has promoted the use of structured observation protocols for identifying faecal contamination hazards at and surrounding rural water sources (World Health Organization 1997). As well as being promoted as a tool for water supply managers, sanitary risk inspection has been used in national water source surveys, such as the Rapid Assessment of Drinking-Water Quality (RADWQ) survey series (World Health Organization and UNICEF 2012)
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