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Bulletin of the World Health Organization logoLink to Bulletin of the World Health Organization
. 2015 Nov 27;94(2):111–121A. doi: 10.2471/BLT.15.162974

Drinking water and sanitation: progress in 73 countries in relation to socioeconomic indicators

Eau potable et assainissement: progrès réalisés dans 73 pays par rapport aux indicateurs socioéconomiques

Agua potable y saneamiento: progreso en 73 países en relación con los indicadores socioeconómicos

مياه الشرب والصرف الصحي: مستوى التقدم في 73 دولة فيما يتعلق بالمؤشرات الاجتماعية والاقتصادية

饮用水和卫生设施: 在 73 个国家中取得的进展与社会经济指标的相关性

Питьевая вода и санитария: прогресс в части социально-экономических показателей на примере 73 стран

Jeanne Luh a,, Jamie Bartram a
PMCID: PMC4763998  PMID: 26957676

Abstract

Objective

To assess progress in the provision of drinking water and sanitation in relation to national socioeconomic indicators.

Methods

We used household survey data for 73 countries – collected between 2000 and 2012 – to calculate linear rates of change in population access to improved drinking water (n = 67) and/or sanitation (n = 61). To enable comparison of progress between countries with different initial levels of access, the calculated rates of change were normalized to fall between –1 and 1. In regression analyses, we investigated associations between the normalized rates of change in population access and national socioeconomic indicators: gross national income per capita, government effectiveness, official development assistance, freshwater resources, education, poverty, Gini coefficient, child mortality and the human development index.

Findings

The normalized rates of change indicated that most of the investigated countries were making progress towards achieving universal access to improved drinking water and sanitation. However, only about a third showed a level of progress that was at least half the maximum achievable level. The normalized rates of change did not appear to be correlated with any of the national indicators that we investigated.

Conclusion

In many countries, the progress being made towards universal access to improved drinking water and sanitation is falling well short of the maximum achievable level. Progress does not appear to be correlated with a country’s social and economic characteristics. The between-country variations observed in such progress may be linked to variations in government policies and in the institutional commitment and capacity needed to execute such policies effectively.

Introduction

The United Nations recognizes the basic human right to water and sanitation.1,2 Accordingly, the international community, through the recent adoption of the Sustainable Development Goals (SDGs), has made a commitment to achieve universal and equitable access to safe drinking water and adequate sanitation by 2030.3 The SDGs build on the Millennium Development Goal (MDG) target4 to halve, between 1990 and 2015, the proportion of the population without access to safe water and basic sanitation. During the MDG period, some countries have made substantial progress, while others have stagnated.5 The national characteristics that may enhance or hinder progress on water and sanitation are poorly understood. For example, external finance should make it easier for governments to improve drinking water and sanitation coverage. While a positive correlation between aid received and improvements in such coverage has been observed in some studies,6,7 other studies have not detected such a relationship.811 The differing results may be due to limitations in the methods used8 and/or the choice of indicator used to measure progress. Progress has been measured as population access to improved drinking water and sanitation – or the change in such access over a specified period. However, changes in population access are not necessarily comparable across different countries because, as a country approaches universal access, it becomes increasingly difficult to reach those who still lack access.

The aim of the present study is to determine whether progress in improving access to improved drinking water and sanitation, achieved by countries between 2000 and 2012, is associated with national socioeconomic characteristics. We used a new indicator of progress – the normalized rate of change in access – to allow countries to be compared, regardless of their initial coverage levels.

Methods

Data sources

We obtained estimates of the percentage of national populations with access to improved sanitation and water – for various years between 2000 and 2012 – from the 2013 Country Files of the Joint Monitoring Programme for Water Supply and Sanitation12 – which were the most up-to-date information available at the time of analyses. This World Health Organization/United Nations Children’s Fund programme compiles the results of nationally representative surveys, including Demographic and Health Surveys, Multiple Indicator Cluster Surveys, World Health Surveys and national censuses. We considered only data from 2000 onwards to reflect the progress countries made since the MDGs were set in the year 2000.

We included shared toilet facilities in our improved-sanitation category because data for both shared sanitation and total improved sanitation including shared sanitation – i.e. the two data sets needed to investigate total improved sanitation excluding shared sanitation – were only available for four of our study countries. The Joint Monitoring Programme currently discounts shared sanitation from total improved sanitation by applying a fixed ratio for each country.13 However, since these ratios are based on data that may have been collected before 2000 and, for some countries, are based on a single data point, we decided not to use them – or any other similar correction factor – in our analyses. We included countries with at least five data points that covered at least three different years. Multiple survey data points from any one year were treated independently.

Indicator of progress

To compare countries with differing initial levels of population access to improved sanitation and water, we defined the progress of country i as its normalized rate of change in access:

normalized ratei,j=ratei,jmin. ratejmax. ratejmin. ratej (1)

where normalized ratei,j is the normalized rate of change for country i that had a baseline coverage level j in the year 2000; ratei,j is the absolute rate of change for country i at coverage level j; max. ratej is the maximum rate achievable by any country at coverage level j (based on historical data, see below) and the min. ratej is set at zero (no progress). Each country’s absolute rate of change was calculated from the earliest available year (2000 in most cases) using linear regression.

We determined values for the maximum rate achievable at each coverage level using the frontier approach.14,15 Historical absolute rates of change for all countries were plotted as a function of the national coverage level for the year 2000. For countries that had survey data for 2000, we used those values for national coverage level. For countries that did not have surveys for 2000, we used estimates from the Joint Monitoring Programme.12 The best-performing countries (which we refer to as frontier points) delineate an upper boundary or frontier against which the performance of the other countries can be compared. We used the frontier efficiency analysis package16 in R software17 to identify frontier points.

A polynomial curve was fitted through the frontier points to obtain the frontier curve – with the requirement that the curve must pass through the point corresponding to 100% coverage and 0% increase in coverage per year. The frontier curve allowed the maximum achievable rates of improvement in water and sanitation coverage to be estimated for all countries, depending on their initial level of coverage (Table 1). Using the estimated maximum achievable rates and Equation 1, we obtained the normalized rates of change for our study countries. The requirement that the frontier curve must pass through the point corresponding to 100% coverage and 0% increase in coverage per year meant that the frontier curve – which is the fitted polynomial equation – sometimes fell below a frontier point. This resulted in a normalized rate greater than 1 for some frontier countries. We assigned a normalized rate of 1 to all such countries. Similarly, for countries in which we found access to improved drinking water and sanitation to be decreasing, we limited the negative normalized rate to –1. All of the normalized rates we report therefore fall between –1 and 1.

Table 1. Population access to improved water and sanitation, linear rates of change and corresponding normalized rates of change, 73 countries, 2000–2012.

Country Drinking water
Sanitation
No. of data points Years R2a 2000 coverage (%) Rate of change
No. of data points Years R2a 2000 coverage (%) Rate of change
Absolute (%/year) Normalized Absolute (%/year) Normalized
Albania 5 2000–2009 0.30 97.1 –0.19 –0.57 5 2000–2009 0.34 90.5 0.47 0.43
Armenia 13 2000–2011 0.49 95.3 0.50 0.93 0
Bangladesh 10 2000–2011 0.76 76.2 0.82 0.42 10 2000–2011 0.83 68.4 1.51 0.77
Belize 5 2000–2009 0.65 89.3 0.85 0.77 5 2000–2009 0.78 90.9 0.50 0.47
Benin 6 2001–2009 0.17 66.1b 0.57 0.25 6 2001–2009 0.90 9.0b 1.45 0.83
Bolivia (Plurinational State of) 10 2000–2009 0.74 80.1 1.00 0.57 11 2000–2009 0.47 58.5 1.13 0.50
Botswana 9 2000–2008 0.34 95.4 0.20 0.37 8 2000–2008 0.48 60.3 0.88 0.40
Brazil 21 2000–2011 0.54 91.8 0.30 0.34 20 2000–2011 0.78 71.6 0.96 0.51
Burkina Faso 11 2003–2010 0.35 59.9b 1.08 0.45 0
Cabo Verde 6 2000–2010 0.86 38.5 1.38 0.44
Cambodia 8 2000–2011 0.51 46.8 1.77 0.72 8 2000–2011 0.92 19.2 1.95 0.64
Cameroon 5 2000–2007 0.35 59.4 1.03 0.42 5 2000–2007 0.06 62.1 –0.38 –0.17
Chad 5 2000–2010 0.47 46.3 0.15 0.06 5 2000–2010 0.02 13.1 0.06 0.02
Chile 5 2000–2009 0.89 94.9 0.47 0.81 5 2000–2009 0.92 92.0 0.57 0.59
Colombia 0 5 2000–2010 0.68 84.2 1.12 0.76
Costa Rica 11 2000–2011 0.16 95.2 0.16 0.29 11 2000–2011 0.67 94.1 0.34 0.44
Côte d’Ivoire 5 2000–2008 0.31 80.6 –0.92 –0.53 5 2000–2008 0.02 40.6 0.20 0.06
Democratic Republic of the Congo 0 5 2001–2010 0.44 22.6b –1.41 –0.44
Dominican Republic 0 6 2000–2010 0.01 92.2 0.03 0.03
Egypt 5 2000–2008 0.83 97.3 0.07 0.23 5 2000–2008 0.97 97.3 0.76 1.0
Estonia 5 2000–2003 0.25 98.9 –0.06 –0.49 10 2000–2004 0.00 98.9 0.01 0.05
Ethiopia 6 2000–2011 0.98 26.2 2.28 1.0 7 2000–2011 0.89 11.9 2.20 0.97
Georgia 0 6 2000–2010 0.70 97.5 –0.22 –0.59
Ghana 9 2000–2008 0.87 66.5 2.29 1.0 9 2000–2008 0.65 59.8 1.96 0.88
Guatemala 7 2000–2009 0.19 86.4 0.41 0.31 6 2000–2009 0.58 80.2 0.66 0.40
Guinea 5 2002–2007 0.20 63.2b 1.13 0.48 5 2002–2007 0.75 14.1b 1.96 0.76
Guyana 5 2000–2009 0.50 88.8 0.50 0.44 5 2000–2009 0.52 86.3 0.48 0.35
Honduras 14 2001–2011 0.75 80.8b 0.75 0.43 7 2001–2011 0.93 64.5b 2.06 0.99
India 9 2000–2011 0.34 83.2 0.44 0.28 9 2000–2011 0.97 31.5 1.48 0.45
Indonesia 12 2001–2010 0.56 77.7b 1.04 0.55 0
Iraq 5 2000–2011 0.33 82.6 0.87 0.54 0
Jamaica 10 2000–2009 0.00 92.4 –0.00 –0.00 10 2000–2009 0.04 97.0 0.03 0.07
Jordan 5 2002–2010 0.10 96.7b –0.14 –0.38
Kenya 7 2000–2010 0.27 52.9 0.70 0.28 7 2000–2010 0.17 50.3 0.51 0.20
Lao People's Democratic Republic 6 2000–2012 0.85 45.4 2.21 0.90 9 2000–2012 0.89 26.6 3.16 0.95
Lesotho 6 2000–2009 0.00 76.2 –0.04 –0.02 5 2000–2009 0.28 32.8 0.25 0.08
Liberia 6 2000–2011 0.30 60.5 1.11 0.46 6 2000–2011 0.15 30.3 0.71 0.22
Madagascar 9 2000–2011 0.78 33.6 1.33 0.56 8 2000–2011 0.15 32.0 0.23 0.07
Malawi 13 2000–2011 0.55 65.5 1.43 0.61 11 2000–2011 0.47 74.6 0.90 0.50
Mali 5 2001–2010 0.93 45.5b 3.47 1.0 6 2001–2010 0.20 18.2b 0.32 0.11
Mauritania 5 2000–2007 0.04 36.8 0.42 0.17 5 2000–2007 0.84 27.1 1.51 0.42
Mexico 9 2000–2010 0.52 87.2 0.78 0.61 11 2000–2010 0.55 81.7 1.06 0.67
Mongolia 5 2000–2007 0.77 66.8 1.54 0.67 0
Morocco 10 2000–2007 0.88 74.0 1.29 0.63 0
Mozambique 5 2003–2009 0.58 41.1b 1.48 0.61 8 2001–2009 0.45 14.1b 1.10 0.43
Myanmar 0 6 2000–2010 0.43 71.4 1.28 0.68
Namibia 5 2000–2007 0.21 77.6 0.80 0.43
Nepal 7 2001–2011 0.11 77.4b 0.32 0.17 9 2000–2011 0.73 28.5 2.19 0.66
Nicaragua 5 2001–2006 0.48 80.0b 0.56 0.32 0
Niger 5 2000–2008 0.08 43.3 0.44 0.18 0
Nigeria 10 2000–2011 0.55 54.0 0.77 0.31 10 2000–2011 0.44 63.9 –1.02 –0.49
Pakistan 12 2002–2009 0.02 88.3b 0.15 0.13 9 2002–2008 0.86 37.4b 2.30 0.73
Paraguay 6 2000–2004 0.23 77.0 0.95 0.49 5 2000–2004 0.12 65.2 0.87 0.42
Peru 6 2000–2009 0.04 83.0 0.14 0.09 6 2000–2009 0.01 68.8 0.09 0.05
Philippines 6 2000–2008 0.21 91.3 –0.15 –0.16 6 2000–2008 0.51 81.4 0.52 0.33
Republic of Korea 7 2000–2006 0.99 93.5 0.50 0.69 0
Republic of Moldova 13 2000–2010 0.40 93.0 0.35 0.46 13 2000–2010 0.73 84.4 0.88 0.60
Rwanda 11 2000–2010 0.00 68.7 0.06 0.03 10 2000–2010 0.84 52.0 2.56 1.0
Samoa 5 2001–2011 0.66 93.3b 0.89 1.0 0
Senegal 7 2000–2011 0.66 67.3 0.77 0.34 8 2000–2011 0.46 56.3 0.82 0.35
Sierra Leone 5 2003–2010 0.89 46.8b 1.28 0.52 7 2000–2011 0.33 37.0 0.67 0.21
South Africa 7 2000–2008 0.83 85.1 0.71 0.49 8 2000–2008 0.13 74.3 0.58 0.32
Sri Lanka 7 2000–2010 0.70 74.6 1.25 0.62 5 2000–2010 0.61 89.2 1.06 0.90
Swaziland 5 2000–2010 0.59 51.8 1.21 0.49 6 2000–2010 0.48 68.4 0.71 0.36
Tajikistan 6 2000–2009 0.18 59.1 0.54 0.22 5 2000–2007 0.62 59.1 0.80 0.35
Thailand 5 2000–2006 0.20 93.2 0.26 0.35 5 2000–2006 0.16 99.1 –0.04 –0.27
Timor-Leste 6 2001–2010 0.52 54.3b 1.35 0.55 6 2001–2010 0.02 37.4b 0.17 0.05
Uganda 10 2001–2010 0.77 56.8b 1.61 0.66 11 2000–2010 0.51 48.1 0.68 0.25
United Republic of Tanzania 10 2000–2011 0.00 55.5 –0.03 –0.01 10 2000–2011 0.70 14.0 0.88 0.34
Uruguay 5 2003–2011 0.00 97.9b –0.01 –0.03 5 2003–2011 0.73 96.7b –0.16 –0.34
Viet Nam 8 2000–2011 0.82 78.8 1.20 0.66 8 2000–2011 0.52 61.2 1.20 0.55
Zambia 6 2002–2010 0.61 53.6b 1.04 0.42 7 2000–2010 0.02 56.9 0.11 0.05
Zimbabwe 5 2003–2011 0.09 79.6b –0.29 –0.17 5 2003–2011 0.16 40.4b –0.34 –0.11

a A measure of goodness of fit for the linear regression.

b Estimates from the Joint Monitoring Programme for Water Supply and Sanitation.12

Regression analyses

We used regression analyses to investigate the relationship between progress in water and sanitation and the following national socioeconomic indicators: (i) gross national income per capita – in current United States dollar (US$) values that had been derived using the Atlas method;18 (ii) government effectiveness;19 (iii) the per-capita level of official development assistance for sanitation and water – calculated, in constant 2011 values, by dividing the total assistance disbursed from all donors20 by the total population;21 (iv) the volume of renewable internal freshwater resources per-capita;18 (v) the percentage of the female population older than 25 years that had completed secondary education;22 (vi) the percentage of the population with a daily income of less than US$ 1.25;18 (vii) the Gini coefficient;18 (viii) the mortality rate among children younger than five years;18 and (ix) the human development index – a composite index reflecting life expectancy, education and income.23 For each indicator and country, we used the value for the year 2000 or, if that value was not available, that for the closest available year.

We initially considered data from the World Health Organization’s Global Analysis and Assessment of Sanitation and Drinking Water reports, which provide policy and economic indicators such as the per-capita budget for drinking water and sanitation from the year 201024 and per-capita expenditure on sanitation and water in the year 2014.25 However, as these data relate to time periods that are at least 10 years off from our target year of 2000 – and indicators such as expenditures per capita may vary substantially from year to year – we decided not to include them in our analyses.

Several of the nine national characteristics we investigated were highly correlated. We therefore used principal components analysis on the nine national indicators to obtain uncorrelated synthetic independent variables (Table 2). However, based on the Kaiser criterion, we only used the three synthetic variables that gave eigenvalues greater than 1 – which together accounted for 76% of the variance in the data observed – in our regression analyses. Backward stepwise regression – with P-values of 0.05 and 0.10 for the addition and deletion of variables, respectively – was also used to identify a subset of the three synthetic independent variables for the regression analyses.

Table 2. Results of principal component analysis based on nine national socioeconomic indicators for all 73 study countries.

Indicator Component
1 2 3 4 5 6 7 8 9
Gini coefficient 0.157 0.660 0.353 0.217 0.295 –0.445 –0.165 –0.230 0.050
Proportion of population with daily income below US$ 1.25a –0.407 0.174 –0.011 –0.032 0.443 0.322 –0.513 0.490 0.005
Mortality rate among children aged < 5 years –0.434 0.175 0.127 –0.015 0.104 –0.066 0.693 0.249 0.455
Per-capita volume of renewable internal freshwater resources 0.088 0.576 –0.523 0.357 –0.299 0.395 0.115 0.011 –0.036
Per-capita gross national income 0.440 0.124 0.157 –0.116 –0.167 –0.186 0.154 0.755 –0.313
Government effectiveness 0.316 0.051 0.555 –0.059 0.155 0.709 0.190 –0.153 –0.013
Per-capita level of official development assistance for sanitation and water –0.169 –0.268 0.365 0.806 –0.282 0.000 –0.110 0.156 0.013
Percentage of the female population older than 25 years that had completed secondary education 0.280 –0.264 –0.328 0.396 0.697 –0.038 0.282 0.037 –0.142
Human development index 0.462 –0.107 –0.108 0.021 –0.027 0.013 –0.254 0.162 0.820
Eigenvalue 4.395 1.318 1.089 0.896 0.597 0.391 0.194 0.091 0.029
Proportion 0.488 0.146 0.121 0.010 0.066 0.044 0.022 0.010 0.003
Cumulative 0.488 0.635 0.756 0.855 0.922 0.965 0.987 0.997 1.000

US$: United States dollars.

a As defined by the World Bank.18

Univariate and multivariate regression analyses were performed in Stata version 12 (Stata Corp. LP, College Station, United States of America). We ran models using the data from all of our study countries and, separately, using only the data from those study countries that had no armed conflict between 2000 and 2012.26 While regression results do not necessarily provide information on causality, a predictive empirical model could be useful in estimating the progress towards universal access in countries where sanitation and water data are not available. We analysed the relationship between the normalized rates of change and the nine national indicators that we investigated, as independent variables, using a linear model:

normalized rate=β1x1+β2x2++βixi+constant (2)

and a fractional logistic model:

lognormalized rate1normalized rate=β1x1+β2x2++βixi+constant (3)

where β1 to βi are the fitted model coefficient values and x1 to xi are the independent variables. Countries with negative normalized rates were excluded from the fractional logistic regressions because, for these, the output parameter must lie between 0 and 1. These regressions therefore focused only on countries that had made progress in increasing access to improved sanitation and water. We re-ran the models using the synthetic independent variables.

Country pairings

We selected countries where, despite similar initial coverage, we observed marked differences in progress. To understand possible reasons for these differences in progress, we chose discordant pairs of countries within the same geographic region and with similar characteristics – as defined by the country clusters of Onda et al.27 – and compared their national socioeconomic indicators.

Results

National access to improved sanitation and water in the year 2000 and historical absolute rates of change are shown in Table 1. Relatively few relevant data were available from high-income countries that are approaching or have already achieved universal access. High-income countries were therefore not well represented in our analyses. The absolute rates of change in access to improved drinking water and sanitation ranged from –0.9% to 3.5% per year (67 countries) and from –1.4% to 3.2% per year (61 countries), respectively.

The frontier curves used to calculate the maximum rates of change in Equation 1 – shown as solid lines in Fig. 1 – were constructed using five frontier points for water – based on data from Armenia, Egypt, Ethiopia, Ghana and Samoa – and eight frontier points for sanitation – based on data from Benin, Egypt, Estonia, Ethiopia, Honduras, Lao People's Democratic Republic, Rwanda and Sri Lanka. For water, Mali was identified as an outlier28,29 and not used to construct the frontier curve. The frontier curves for both sanitation and water indicate decreases in the maximum achievable rate of change as countries approach 100% coverage.

Fig. 1.

Historical absolute rates of change in access to sanitation and drinking water, 2000–2012

Notes: Rates were calculated for 2000–2012, and are shown as a function of the national coverage in the year 2000. Each data point represents a different country – 67 for water and 61 for sanitation – but only the names of some of the countries with particularly good or poor rates of change are shown.

Fig. 1

While positive and negative absolute rates indicate countries with increasing and decreasing coverage, respectively, only the normalized rates in Table 1 should be used to compare the performances of the study countries. These normalized rates indicate that, over our study period and for both water and sanitation, only about one in every three of our study countries progressed at a rate that was at least half of their maximum achievable rate – i.e. they had normalized rates that were greater than 0.5. Among the countries with relevant data, 20 (30%) of 67 had normalized rates for water that fell below 0.25 and 21 (34%) of 61 had the same low normalized rates for sanitation.

Using the normalized rate as our indicator of progress, only two univariate regression models for access to drinking water – and no models for sanitation – were statistically significant overall (P ≤ 0.05; Table 3). However, the model fit was poor (adjusted R2 < 0.2) and Fig. 2 and Fig. 3 show the poor agreement between the observed and modelled estimates.

Table 3. Regression model results for the associations between normalized rates of change in improved water and sanitation coverage and socioeconomic indicators.

Model type, coverage typea Independent variable Regression type Inclusion of countries with armed conflict? n Coefficient SE (95% CI)
Univariate
Water Povertyb Linear Yes 63 0.004 0.0018 (0.0004 to 0.0077)
Water Gini coefficient Linear No 27 0.015 0.0068 (0.0010 to 0.0291)
Multivariate
Sanitation Component 2c Linear Yes 50 –0.0903 0.0449 (–0.1801 to –0.00004)
Water Component 2c Linear No 23 0.124 0.0573 (0.0048 to 0.2433)

CI: confidence interval; SE: standard error.

a Only the results for regressions that gave P-values of no greater than 0.05 are shown.

b Proportion of the population with daily income below 1.25 United States dollars.

c Second component obtained from principal components analysis (Table 2).

Fig. 2.

Observed and modelled normalized rates of change in access to drinking water in 63 countries, 2000–2012

Notes: The plot shows estimates from a linear regression in which the proportion of the population with a daily income below 1.25 United States dollars was used as the independent variable. The solid line indicates a perfect match between the observed rates and the modelled estimates.

Fig. 2

Fig. 3.

Observed and modelled normalized rates of change in access to drinking water in 27 countries with no armed conflict, 2000–2012

Notes: The plots show estimates from linear regressions, with either the Gini coefficient or the second component from principal components analysis used as the independent variable. The solid lines indicate a perfect match between the observed rates and the modelled estimates.

Fig. 3

Multivariate regression with the three synthetic independent variables resulted in two models – i.e. one for water and one for sanitation – that were statistically significant (Table 3). Again, however, there was poor agreement between the observed and the modelled estimates (Fig. 3 and Fig. 4).

Fig. 4.

Observed and modelled normalized rates of change in access to sanitation in 50 countries, 2000–2012

Notes: The plot shows estimates from a linear regression in which the second component from a principal components analysis was used as the independent variable. The solid line indicates a perfect match between the observed rates and the modelled estimates.

Fig. 4

Overall, our results show no correlation between the normalized rates of change in the improvement of access to drinking water or sanitation and any of the nine national indicators that we investigated or any of the principal components obtained from these indicators. A similar lack of correlation was observed when the analyses were performed using the most recent data available for each of the nine national indicators (available from the corresponding author).

An analysis of the illustrative pairs of countries with differing progress indicate that no single indicator was consistently associated with progress in coverage for water or sanitation (Table 4 or Table 5, respectively, available at: http://www.who.int/bulletin/volumes/94/2/15-162974).

Table 4. Comparison of selected national socioeconomic indicators in pairs of countries with differing progress in drinking water coverage, 2000–2012.

Characteristic Pair 1
Pair 2
Pair 3
Egypt Jordan Philippines Thailand United Republic of Tanzania Uganda
Country clustera 3 3 4 4 5 5
Geographical area Eastern Mediterranean Eastern Mediterranean South-east Asia South-east Asia East Africa East Africa
Normalized rate 0.23 –0.38 –0.16 0.35 –0.01 0.66
Initial coverage (%) 97.3 96.7 91.3 93.2 55.5 56.8
Per-capita gross national income (current US$) 1471 1797 1048 1959 297 264
Per-capita level of official development assistance for sanitation and water (constant 2011 US$) 1.91 12.4 0.15 0.11 1.04 1.44
Per-capita volume of renewable internal freshwater resources (m3) 26.4 135.4 5917 3519 2346 1503
Gini coefficientb 32.8 36.4 46.1 42.8 34.6 43.1
Government effectivenessc –0.16 –0.01 –0.14 0.20 –0.42 –0.38

US$: United States dollars.

a As defined by Onda et al.27

b The lower the Gini coefficient, the greater the equality.

c As defined by the World Bank.19 The higher the value, the stronger the performance of governance.

Table 5. Comparison of selected national socioeconomic indicators in pairs of countries with differing progress in sanitation coverage, 2000–2012.

Characteristic Pair 1
Pair 2
Pair 3
Costa Rica Dominican Republic Paraguay Peru Kenya Rwanda
Country clustera 3 3 4 4 5 5
Geographical area Central America and the Caribbean Central America and the Caribbean South America South America East Africa Central/East Africa
Normalized rate 0.44 0.03 0.42 0.05 0.20 1.0
Initial coverage (%) 94.1 92.2 65.2 68.8 50.3 52.0
Per-capita gross national income (current US$) 3704 2596 1346 2052 421 233
Per-capita level of official development assistance for sanitation and water (constant 2011 US$) 0.13 0.61 0.07 0.65 0.85 0.84
Per-capita volume of renewable internal freshwater resources (m3) 27 456 2350 16 872 60 457 627 1057
Gini coefficientb 46.5 52.0 57.0 50.8 42.5 51.5
Government effectivenessc 0.25 –0.33 –1.17 –0.09 –0.54 –0.65

US$: United States dollars.

a As defined by Onda et al.27

b The lower the Gini coefficient, the greater the equality.

c As defined by the World Bank.19 The higher the value, the stronger the performance of governance.

Discussion

The historical absolute rates of change in access to sanitation and water varied greatly at all coverage levels. Over our study period, most countries increased their sanitation and water coverage. Ethiopia and the Lao People's Democratic Republic, for example, showed absolute rates of change – in access to both drinking water and sanitation – in excess of  2.2% per year. Although several countries were found to have decreasing sanitation or water coverage, only one of the countries we investigated – Zimbabwe – showed decreasing coverage for both sanitation and water. We determined normalized rates of change to compare progress between countries. For example, while both Kenya and South Africa had an absolute rate of change of 0.70% per year for water, the corresponding normalized rate for Kenya (0.28) was markedly lower than that for South Africa (0.49) – indicating that South Africa was making greater progress than Kenya.

National socioeconomic characteristics may not be primary determinants of progress in access to water and sanitation. For example, from the illustrative country pairings, Peru might be expected to make better progress than Paraguay – since, per capita, Peru has the greater gross national income, external financial assistance and renewable freshwater resources. However, the normalized rates that we calculated indicate that, over our study period, Paraguay was making good progress whereas Peru was making no progress. Factors other than the nine national indicators we investigated are probably more important than those indicators in determining progress towards universal access. For example, government policies – and variation in the provision of the institutional commitment and capacity needed to execute such policies effectively – may be important determinants of such progress. The lack of association we observed between progress and per-capita level of official development assistance is consistent with previous studies811 – although these earlier investigations used different measures of progress and varied in their scale, from global to city level.

Our study has several limitations. We calculated absolute rates of change in coverage of water and sanitation using a linear fit to the data points – even though progress may have been nonlinear during our study period. This may affect the estimated rates of change, the identification of frontier countries and consequently, the frontier curve, the corresponding maximum rates and the normalized rates. Household surveys used as our data sources did not include extra-household settings – e.g. educational institutions, workplaces and health-care settings – and therefore did not represent sanitation and water access for all dimensions of society. Neither did the surveys distinguish between the different levels of improved sanitation or water services – e.g. between a household tap and a community hand pump or between a pit latrine and a sewer connection. Furthermore, inequalities in access often exist. Coverage and service levels tend to be relatively poor among marginalized and vulnerable groups and this may not be captured by national surveys. Identification of the disadvantaged groups in each country is needed so that progress among these groups can be compared with that in the general population.

With respect to our regression analyses, we recognize that the variables we used as national economic indicators may not accurately reflect the levels of investment in sanitation and water. For example, such indicators exclude the many household investments, particularly in sanitation, that occur in developing countries. In addition, the data for the nine national indicators that we investigated were for a single year and did not cover all of our 2000–2012 study period. Alternatives to linear and logistic regression, such as generalized additive models, need to be tested in future studies.

Use of normalized rates allowed countries to be compared regardless of their coverage level, aligns with the human rights principle of progressive realization and could be extended to measure progress in other health sectors – e.g. to measure rates of improvement in the maternal mortality ratio. Use of such quantitative measures of progress allow policy-makers to make evidence-based decisions and provide the human rights community and others with an objective method for country comparison. Our results indicate that, in many countries, the progress being made towards universal access to improved drinking water and sanitation is far from the maximum achievable. The lack of relationship between the normalized rates of change and the nine national indicators that we investigated is important – particularly with respect to the economic variables. The finding that official development assistance is not correlated to our indicator of progress suggests that investment alone is not sufficient to ensure progress. In future studies, the effect on progress of additional variables that assess the enabling environment and governance should be investigated.

Acknowledgements

We thank C Wiesen (Odum Institute, University of North Carolina–Chapel Hill) for helpful discussions on statistical analyses and T Slaymaker for feedback on the manuscript.

Funding:

This research was partially funded by WaterAid UK.

Competing interests:

None declared.

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