Abstract
Shallow alluvial and karst aquifers and widespread inadequate sanitation practices combine to impact water resources in Haiti. The vulnerability of aquifers is complicated by complex cultural, ecological, geological, hydrological, and hydrogeological considerations. Roughly 84% of the rocks exposed in Haiti consist of calcareous rocks and alluvium. These lithologies serve as an efficient reservoir and transport mechanism for water-borne pathogens, which negatively impact the health of many Haitians. Data from 9,837 water points indicate that 75% of the water sources in the Centre, 55% in the Nord (North), and 12% in the Ouest (West) departments are considered unsafe or high risk based on World Health Organization standards. Inadequate sanitation and, in some cases, improper siting and installation of pit latrines contribute to poor water quality. Numerous safe-water intervention technologies exist and are effective at removing pathogens that contaminate water sources; however, many Haitians lack the means to obtain these solutions. Future regional precipitation and climate trends will have important implications for selecting appropriate water sources and safe-water interventions. Additional efforts to collect and compile regional water quality data are needed to better understand country-wide contamination trends and patterns.
Résumé
Les aquifères alluviaux de faible profondeur et les aquifères karstiques, ainsi que les pratiques sanitaires inadéquates et répandues, ont un impact combiné sur les ressources en eau en Haïti. La vulnérabilité des aquifères est. compliquée par des considérations culturelles, écologiques, géologiques, hydrologiques et hydrogéologiques complexes. Environ 84% des affleurements rocheux en Haïti sont constitués de roches calcaires ou d’alluvions. Ces lithologies servent de réservoir efficace et de mécanisme de transport pour les agents pathogènes d’origine hydrique, qui ont un impact négatif sur la santé de nombreux Haïtiens. Les données de 9837 points d’eau indiquent que 75% des sources d’eau dans le Centre, 55% dans le Nord et 12% dans les départements de l’Ouest sont considérées comme dangereuses ou à haut risque selon les normes de l’Organisation mondiale de la santé. Un assainissement inadéquat et, dans certains cas, un emplacement et une installation inappropriés des latrines à fosse contribuent à la mauvaise qualité de l’eau. De nombreuses technologies d’intervention pour rendre l’eau salubre existent et sont efficaces pour éliminer les agents pathogènes qui contaminent les sources d’eau; cependant, de nombreux Haïtiens n’ont pas les moyens d’obtenir ces solutions. Les futures tendances régionales en matière de précipitations et de climat auront des implications importantes pour la sélection des sources d’eau appropriées et des interventions pour rendre l’eau salubre. Des efforts supplémentaires pour collecter et compiler des données régionales sur la qualité de l’eau sont nécessaires pour mieux comprendre les tendances et les schémas de contamination à l’échelle nationale.
Resumen
Los acuíferos aluviales y kársticos poco profundos y las generalizadas prácticas de saneamiento inadecuadas se combinan para afectar a los recursos hídricos en Haití. La vulnerabilidad de los acuíferos se complica por complejas consideraciones culturales, ecológicas, geológicas, hidrológicas e hidrogeológicas. Aproximadamente el 84% de las rocas expuestas en Haití consisten en rocas calcáreas y aluviones. Estas litologías sirven de depósito y mecanismo de transporte eficaces para los patógenos transmitidos por el agua, que afectan negativamente a la salud de muchos haitianos. Los datos de 9837 puntos de agua indican que el 75% de las fuentes de agua en el Centro, el 55% en el Norte y el 12% en el Oeste se consideran inseguras o de alto riesgo según las normas de la Organización Mundial de la Salud. Un saneamiento inadecuado y, en algunos casos, una ubicación e instalación incorrectas de las letrinas de pozo contribuyen a la mala calidad del agua. Existen numerosas tecnologías de intervención para el agua potable que son eficaces para eliminar los agentes patógenos que contaminan las fuentes de agua; sin embargo, muchos haitianos carecen de medios para obtener estas soluciones. Las futuras precipitaciones regionales y las tendencias climáticas tendrán importantes implicancias para la selección de las fuentes de agua adecuadas y las intervenciones de agua segura. Se necesitan esfuerzos adicionales para recoger y compilar datos regionales sobre la calidad del agua para comprender mejor las tendencias y patrones de contaminación en todo el país.
摘要
浅层冲积层和喀斯特含水层以及普遍存在的卫生规范不足共同影响了海地的水资源。含水层的脆弱性因复杂的文化、生态、地质、水文和水文地质因素而变得复杂。海地大约 84% 的岩石由钙质岩石和冲积层组成。这些岩性是水传播病原体的有效储层和运输通道, 对许多海地人的健康产生不利影响。来自 9837 个取水点的数据表明, 根据世界卫生组织的标准, 中部 75% 的水源、Nord(北部)55%的水源和Ouest(西部)12%的水源被认为是不安全或高风险的。卫生设施不足, 在某些情况下, 坑式厕所的选址和安装不当会导致水质变差。存在许多水安全防治技术, 并能有效去除污染水源的病原体;然而, 许多海地人缺乏获得这些解决方案的手段。未来的区域降水和气候趋势将对选择合适的水源和水安全防治产生重要影响。需要进一步努力收集和汇编区域水质数据, 以更好地了解全国范围的污染趋势和模式。
Resumo
Aquíferos rasos aluviais e cársticos e práticas de saneamento difundidas de maneira inadequada combinam-se para impactar os recursos hídricos no Haiti. A vulnerabilidade dos aquíferos é complicada por complexas considerações culturais, ecológicas, geológicas, hidrológicas e hidrogeológicas. Aproximadamente 84% das rochas expostas no Haiti consistem de rochas calcárias e aluviões. Essas litologias servem como um eficiente reservatório e mecanismo de transporte para patógenos transmitidos pela água, que impactam negativamente a saúde de muitos haitianos. Dados de 9837 pontos de água indicam que 75% das fontes de água no centro, 55% no Norte e 12% no Oeste são consideradas inseguras ou de alto risco com base nos padrões da Organização Mundial da Saúde. O saneamento inadequado e, em alguns casos, a localização e instalação inadequadas de latrinas de fossa contribuem para a má qualidade da água. Existem inúmeras tecnologias para intervenção em água potável que são eficazes na remoção de patógenos que contaminam as fontes de água; no entanto, muitos haitianos carecem de meios para obter essas soluções. As futuras tendências regionais climáticas e de precipitação terão implicações importantes na seleção de fontes de água apropriadas e de intervenções na água potável. Esforços adicionais para coletar e compilar dados regionais de qualidade da água são necessários para entender melhor as tendências e padrões de contaminação em todo o país.
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Introduction
Haiti, a country of approximately 11 million people, occupies the western one-third of the island of Hispaniola in the Caribbean (Fig. 1). Haiti was a productive and lucrative colony of France until plantation slaves rebelled and gained their independence in 1804. Post-colonial governance and land ownership, combined with internally and externally imposed economic isolation, have resulted in a large number of subsistence farmers working small plots of land. The majority of these small holdings lack sanitation or water irrigation infrastructure and are often used for grazing livestock and charcoal production (Ghilardi et al. 2018).
The Haiti earthquake of January 2010 and rapid post-earthquake emergence of cholera (Vibrio cholerae) focused renewed attention on water resources in Haiti, as well as the endemic problems with sanitation and pathogen transmission in shallow aquifers, springs, and surface waters. The medical community and those who have researched water in Haiti are engaged in ongoing discussions about how best to combat cholera and other water-borne pathogens. One issue is whether to invest scarce resources in vaccination and medical treatment or to invest in longer-term improvements through environmental restoration, sanitation, and safe-water interventions such as filters and other water treatments options (Butler 2011; Cyranoski 2011; Farmer and Ivers 2012; Periago et al. 2012; Piarroux et al. 2011; Wampler 2011).
Poor sanitation practices, combined with shallow aquifers and fractured rocks, result in widespread contamination of shallow groundwater, springs, and surface-water sources (Balthazard-Accou et al. 2017; Gelting et al. 2013; Rebaudet et al. 2017; Schram and Wampler 2018; Wampler and Sisson 2011). Loss of soil, forest cover, and primary forest have led to dysfunctional macro- and micro-biotic ecosystems contributing to a cycle of ineffective contaminant removal and recontamination with pathogens after rain events (Churches et al. 2014; Hedges et al. 2018; Wampler et al. 2019). It is clear that any water resource and sanitation solutions implemented in Haiti need to be transdisciplinary, with a good understanding of the complex culture, ecology, geology, hydrology, and hydrogeology which impact water quality in Haiti (Wampler et al. 2016).
Most areas in Haiti lack sanitation facilities, and in many rural areas, large-scale safe-water infrastructure and sanitation improvements are not feasible. As a result, many nongovernmental organizations (NGOs) are choosing to direct efforts toward point of use (POU), household water treatment (HWT), and pit latrine installations (Rayner et al. 2016; Widmer et al. 2014). Most of these solutions require continued support, education, and maintenance to remain effective (Lask et al. 2015, Mukherjee et al. 2016, Sisson et al. 2013a, b). Although some improvements in sanitation and water have been made in Haiti, as of 2017, 36% of the rural population still practice open defecation and 40% are using unimproved water sources resulting in widespread transmission of water-borne pathogens and poor health outcomes (Table 1).
Abundant water borne pathogens, poor sanitation, and karst aquifer pathways providing rapid and unattenuated contamination transmission, represent a unique and deadly combination for Haitians. This report provides an overview of the geology, hydrogeology, karst processes, and karst landforms in Haiti and their contributions to contaminated water resources. Water quality data from the Artibonite, Nord (north), Ouest (west), and Centre departments of Haiti are presented. Several safe-water interventions are evaluated in terms of cost, sustainability, and compatibility. Recommendations are provided for future deployment and support of safe-water interventions which are culturally compatible and sustainable for Haiti.
Geologic setting and hydrogeology
The island on which Haiti is located, Hispaniola, is a mountainous and tectonically active island with folded rocks, earthquakes, and uplifted coral reefs and submarine basalt (Possee et al. 2019; Wang et al. 2018). Complex folding, faulting, mountain building, and brittle deformation of the rocks in much of Haiti is the results of transpressional forces between the North American and Caribbean tectonic plates, extending and dissecting the island (Wang et al. 2018). The deadly earthquake of January 2010 and recent earthquake of 14 August 2021, are reminders of the active tectonic forces that are still shaping the island of Hispaniola (Bilham 2010; Dupuy 2010; Farmer 2012; Kaya et al. 2011; Mercier de Lépinay et al. 2011; Shan et al. 2011; Sheller et al. 2014).
The geology of Hispaniola consists of a core of intrusive igneous rocks which forms the backbone of the island, near the northern border between Haiti and the Dominican Republic. This core is surrounded by uplifted and deformed sedimentary limestones and shales, volcanic and volcaniclastic rocks, and valley-filling alluvium in a series of roughly east–west-trending mountain ranges (Fig. 2). The details of the geology of Haiti have been well described by previous researchers (Hadden and Minson 2010; Jones 1918; Maurrasse 1982; Woodring et al. 1924). This report will focus mainly on the limestone formations, karst features, and the karst aquifers and springs that serve as a primary water source for many rural Haitians.
Bedrock lithologies in Haiti are dominated by calcareous rock units and alluvium which make up roughly 84% of the surface area of Haiti (Table 2). These lithologies often contain shallow unconfined aquifers that are susceptible to contamination by inadequate sanitation services and by improperly placed or constructed pit latrines.
Many of the durable limestones have fissures and fractures which have been enlarged by dissolution in a process typically referred to as karstification or simply “karst” (Ford and Williams 2013; Kambesis and Despain 2019; Fig. 3). Lack of protective soil cover in many parts of Haiti due to deforestation and erosion has made many unconfined karst aquifers particularly vulnerable to contamination with water-borne pathogens (Alscher 2011; Churches et al. 2014; Hedges et al. 2018; Kennedy et al. 2016; Trček 2007; Wampler et al. 2019). Karst development and dissolution is enhanced locally by faulting, folding, and deformation associated with tectonic forces (Wang et al. 2018).
The development of karst dissolution cavities and caves varies considerably in different limestone units with some exhibiting extensive caves and karst conduits, while others have almost no karst or evidence of karst dissolution. No systematic mapping of the cave formations has been identified; however, available mapping suggests there are at least 150 caves located in several regions with greater cave and karst density (Figs. 2 and 4).
In many karst regions, well-developed weathering of limestone and thick soils, collectively referred to as epikarst, serves as an important primary filter for pathogens (Bakalowicz 2004; Trček 2007). Haiti is exceptional in that many limestone outcrops have thin to nonexistent soil cover. Removal of the natural filtration system is primarily the result of erosion, deforestation, and agricultural practices.
Near major rivers, and in the large basin occupied by Port au Prince, sufficient alluvium has accumulated to form alluvial fans and extensive alluvial aquifers and floodplains. These aquifers, although more effective at filtering pathogens than karst limestone, are also prone to contamination from the installation of shallow hand-dug wells in many rural and semiurban settings (Schram and Wampler 2018).
Water resources and climate
Haiti receives a sufficient volume of water each year to support its growing population (Knowles et al. 1999); however, the precipitation that falls on Haiti is not evenly distributed geographically or temporally (Table 3; Fig. 5).
Haiti has two distinct rainy seasons, in May/June and in September/October (Fig. 6). Total precipitation also varies considerably by region with wet and dry seasons more pronounced in some regions than others—for example, in the northwest corner of Haiti near Môle St. Nicholas, the amount and timing of rainfall are significantly different than in Mirebalais, north of Port au Prince (Fig. 6). Observed differences are likely due to a combination of orographic effects and a prevailing wind direction from the east. Regional precipitation differences have important implications for selecting appropriate water sources and safe-water interventions in different regions of Haiti.
Extensive deforestation and soil loss has resulted in decreased infiltration and aquifer recharge (Alscher 2011; Hernandez-Leal et al. 2006; Reyes-Ortiz et al. 2014). The causes of deforestation are primarily land clearing for agriculture, charcoal production, and urbanization. Decreased natural filtration of surface runoff combined with inadequate sanitation infrastructure, shallow karst aquifers, and dysfunctional macro- and micro-biotic ecosystems, result in widespread contamination of surface-water and groundwater resources with human pathogens (Gerges et al. 2016; Koski-Karell et al. 2016; Rayner et al. 2016; Reyes-Ortiz et al. 2014; Wampler and Sisson 2011). Karst solution of limestone, and abundant fracturing due to brittle deformation, exacerbate this problem by providing pathways, open conduits, storage locations, and rapid transport for bacteria-laden water and organic debris. Biofilms may also be present in underground cavities which allow bacteria and other pathogens to survive in the subsurface and reemerge when groundwater flow increases during the rainy seasons (Dussart-Baptista et al. 2003).
Infrastructure in Haiti is very poor and struggles to support healthy citizens, business development, freedom of movement, and education. Many rural Haitian households and villages do not have running water, power or sanitation. Water resource interventions such as wells, rain water cisterns, spring capping, and reservoirs, are routinely installed by NGOs and local communities; however, maintenance and support for these interventions is often lacking, resulting in failure. Water treatment and storage is also problematic as most methods employed such as chlorination tablets, biosand filters, fiber membrane filters, and other methods, require regular support to remain sustainable.
Materials and methods
Data for this report were compiled from field measurements collected by research teams, government and NGO, and government sources. Water samples from hand-dug wells in rural Haiti were analyzed using the Colilert method and IDEXX quanti-trays to determine total coliform and Escherichia coli (E. coli) bacterial contamination (Kinzelman et al. 2005).
Since 2015, the Direction Nationale de l’Eau Potable et de l’Assainissement (DINEPA) and regional teams of workers (Office Régional d’Eau Potable et d’Assainissement (OREPA)) have collected data from water points in an effort to create a comprehensive database. Data format, quality, and availability vary considerably between departments and teams collecting data. Water point inventories were performed by the NGOs Haiti Outreach and World Vision in partnership with OREPA Ouest, OREPA Nord, and OREPA Centre. The water point inventories were performed to facilitate department-level action planning for water and sanitation access. Water quality parameters such as pH, electrical conductivity, and temperature were recorded in the field with an Oakton PCSTestr 35 multi-parameter probe. Flow was measured using various methods including bucket/stopwatch, area/velocity method for concentrated flows, and in some cases were estimated when direct measurement was not feasible. Aquagenx CBT II EC test kits were used for bacterial analysis on many of the water points; however, some unprotected springs that were not currently used as principal water sources were not analyzed for bacteria.
Results
Data on water sources in Haiti are difficult to obtain. Data collection and analysis methods vary from location to location, making systematic quantitative analysis of water contamination more challenging. Department data, along with original data collected from hand-dug wells and other water sources in rural Haiti provide a partial and imperfect account of groundwater contamination in Haiti.
Water source contamination
Since 2011, water samples from a range of different water sources have been collected and analyzed for E. coli in the Artibonite Department near Verrettes, Haiti (Figs. 1 and 7). Water sources sampled include rivers, undeveloped springs, developed springs, hand-dug wells, shallow hand-pump wells, deep wells, water reservoirs, and water treatment systems (Figs. 8 and 9). The top three most contaminated water sources are rivers, hand-dug wells, and uncapped or unprotected springs. Twenty hand-dug wells were sampled for bacteria in 2016, with only two of these wells having acceptable E. coli levels for drinking water based on World Health Organization Standards (WHO) drinking water standards. The geometric mean of all the wells was 218.8 most probable number (MPN)/100 ml, which is greater than the United States Environmental Protection Agency (US EPA) acceptable body contact standard of 126 cfu/100 ml (Schram and Wampler 2018; US EPA 2012; Table 4).
Aquifer and spring mapping indicate that many rural springs in mountainous areas emerge from alluvial aquifers, carbonate rocks, karst conduits, and cavities. Approximately 75.9% of all mapped springs emerge from alluvial and carbonate aquifers (Table 5).
Department water-point data
Teams from three departments, Ouest, Centre, and Nord, collected and compiled data from 15,581 water points (Table 6). Water sources sampled included borehole or tube wells, piped water sources, protected dug wells, protected springs, rainwater, unprotected dug wells, and unprotected springs. Average conductivity is within a typical range for groundwater with the exception of the Ouest Department, where elevated conductivity may be due to saltwater intrusion into shallow alluvial aquifers. Average groundwater temperature is rather high (Avg. 26.8 °C), which may contribute to pathogen survival in shallow groundwater systems.
A subset of water points (9837) have semiquantitative E. coli MPN data determined using the Aquagenx bag method (Aquagenx 2013). This method provides a range of values from 0 to greater than 100 MPN, and has been used to classify the risk of different water sources based on WHO classification (Table 7).
Based on these data, 75% of the water sources in the Centre, 55% in the Nord, and 12% in the Ouest departments are considered unsafe or high risk. Mapping of WHO risk for 4,706 water points in the Centre Department revealed clusters of high-risk water points. This is consistent with clusters of higher population density and inadequate sanitation (Fig. 10).
Discussion
In many developed nations, improved water quality in karst areas is achieved through land-use management laws that provide source water and recharge area protection. However, land management and source water protection, as practiced in many developed nations, may be difficult to implement in Haiti. Laws regulating land-use are rare, especially in rural areas where enforcement and oversight is difficult. Subsistence farmers, although aware of contamination potential near springs, are often less familiar or aware of the need to protect recharge and source-water areas.
The vulnerability and contamination in aquifers and surface water in Haiti make some form of treatment necessary to reduce negative health outcomes for both rural and urban populations. Addressing these water resource challenges will require an informed approach to selecting, implementing, and supporting safe water treatment methods. River contamination with pathogens is likely due to the common practice of bathing and washing clothing in rivers, uncontrolled livestock grazing, and runoff of fecal matter from open defecation into streams. Open defecation and unprotected shallow hand-dug wells are primary contamination sources for unconfined shallow groundwater aquifers. Spring capping is a common practice; however, bacterial contamination in protected springs is only modestly lower than in unprotected springs (Fig. 7). Many hand-dug wells have no surface collars or covers to prevent contaminated runoff from entering the well. Additionally, most of the water collected from hand-dug wells is collected in buckets and other containers which are lowered into the wells on ropes (Fig. 8). These containers, and the ropes used to lower them, are a significant source of contamination. Another potential source of shallow groundwater contamination is the installation of unlined pit latrines which can result in leaching of contaminated water into unconfined aquifers and karst systems (Fig. 11). The combination of karst development and fractures in limestone make site selection and lining of pit toilets critical to preventing shallow aquifer contamination.
Spring protection through the installation of concrete capping provides some improvement in water quality, although the amount of protection provided does not usually justify the cost and maintenance required to install and maintain a capped spring (Fig. 9). The primary reason for this is that most springs in mountainous areas are fed by shallow karst systems which are susceptible to contamination by open defecation, animal waste, and improperly installed pit latrines. Protecting the site where the spring emerges is unlikely to prevent this distal contamination. In-home treatment methods like biosand filters, chlorination, fiber-membrane filters (Sawyer), and other point-of-use filtration systems, which can be used and maintained by each household, are a more sustainable and suitable means of short-term treatment. The suitability of specific treatment methods is a function of affordability, lifestyle compatibility, distance and availability of water sources, and household water needs. Based on the results presented here, there is clearly a need for in-home treatment or other safe-water interventions as well as increased focus on proper sanitation solutions. Longer-term solutions will require ecological restoration and improved land use laws to protect source water and aquifer recharge areas.
Safe and sustainable treatment methods for Haiti
Providing safe and sustainable water in Haiti is complicated by cultural, geologic, ecologic, sociologic, and economic factors which are described subsequently. Those seeking to provide clean water to Haiti must consider and address these factors to successfully and sustainably provide water for Haitians. Near major rivers and in the large basin occupied by Port au Prince, sufficient alluvium has accumulated to form alluvial fans and alluvial aquifers; however, these are subject to contamination by shallow hand-dug wells (Schram and Wampler 2018). Ecological impacts in the form of deforestation, soil erosion, and a habitat destruction contribute to a hydrologic system which is less able to provide natural filtration for pathogens. An often underappreciated player is the microbiotic ecosystem which is an integral part of the macrobiotic ecosystem (trees and plants), which has also been impacted (Dussart-Baptista et al. 2003; Hwang et al. 2014). Both the microbiotic (beneficial water-borne organisms) and macrobiotic provide a first line of defense for protecting groundwater in Haiti from contamination.
Attitudes and perceptions of water in Haiti are affected by religious attitudes, historic practices, and the general educational level of most rural Haitians (Phelps et al. 2017). Many Haitians who practice Voodoo view water and sources of water as sacred. Waterfalls and springs are generally viewed as sacred places in Voodoo for their natural beauty and provision. Catholicism also views water as sacred, but in a way more connected to God and the cleansing power of water. Both of these viewpoints are predisposed to view water as clean and sacred even when it may be contaminated with pathogens that can kill, especially when those pathogens are not visible and the water appears clean. This widespread perception of water as both sacred and safe is a major challenge for those trying to implement safe water interventions in Haiti.
Haiti is an economically challenged country with many facing daily economic and health challenges. Water in large cities is often provided by central systems of fountains or through vendors of treated water in bottles and bags. In the mountains of Haiti, central water systems and bottled water are not widely available, so many drink untreated water from springs. A simple and effective solution for ensuring the safety of this water would be to boil all water consumed, but many do not have the money to buy fuel for sterilizing water and cooking their meals. Many Haitians are also unaware that the water is unsafe because it looks clean and may be collected from a spring emerging from rock. Numerous water treatment methods are available in Haiti; however, each has pros and cons and may have applicability for some regions more than others (Table 8).
Conclusions and recommendations
Water quality in the shallow unconfined aquifers of Haiti is clearly being impacted by inadequate sanitation infrastructure and practices and, in some cases, improperly installed or located pit latrines. This results in widespread contamination of groundwater with pathogens which negatively impacts the health of many Haitians. POU, HWT, and other water treatment interventions exist; however, many of these solutions require careful selection, education, and follow up to remain sustainable and effective. Climate-change-induced alterations to the already variable precipitation and climate will likely make it more challenging to provide safe and sustainable safe water in Haiti.
The database of water points obtained for this study allowed limited quantitative and qualitative analysis of water contamination at the department level. Similar data are needed across all departments in Haiti so that regional trends can be better understood and reported. Data inconsistencies among departments poses a challenge to this effort. Data will need to be compiled, and quality checked, to ensure that data from different departments are compatible with regional water quality analysis. Regional water quality analysis would be aided by a centralized database into which water quality data could be contributed. Only after widespread collection and compilation of additional data will a country-wide assessment of groundwater contamination be possible. Quantitative bacteriological data, using a method such as the IDEXX Colilert-18, would provide more useful information about bacterial contamination than the semiquantitative Aquagenx bag method. However, the logistics and cost of the IDEXX method may prevent its widespread use.
The distribution, education, and support for POU and HWT options should be decentralized and democratized. This could be achieved through a network of trained resellers operating in a similar manner to the way Digicel Cell Phone company uses “Papa Dap” vendors who resell phone minutes. Each of these independent contractors purchases minutes from Digicel then resells them for a slight profit. This model encourages widespread availability of cell phone minutes, even in rural areas. A similar network of water-treatment-solution vendors could make water treatment tools and support widely available, even in rural areas without NGO intervention or support. Vendor training and support could be offered by local NGOs, DINEPA or OREPA staff, schools, or a combination of these entities.
Biweekly street markets, which take place in most Haitian towns and villages, are a widespread and universal place where Haitians gather to buy and sell food and household items. These markets represent a potentially effective opportunity to distribute, and provide local education and support for POU water-treatment devices. Information and POU products could be provided to market resellers at these community gathering places along with accurate information and support, thus simplifying distribution and support.
Many different strategies and projects to provide safe and sustainable water have been attempted in Haiti, most with limited long-term success. Providing Haitians with inexpensive and readily available POU water treatment at convenient and familiar locations, and in a culturally compatible way, may be the best means of reaching the goal of universal access to clean water in Haiti in the near term. Western-style water treatment infrastructure and water distribution systems, although perhaps more technologically effective, are simply not culturally or economically compatible with most rural Haitian communities.
Long-term and widespread improvement of groundwater quality in Haiti will require changes in land-use management and agricultural practices to reduce deforestation, erosion, and soil loss. Other long-term solutions include the installation of properly constructed deep wells (>30 m) near populated areas, conversion of hand-dug wells to in-situ filtration wells, development of a network of community-based water experts to support/maintain in-home treatment methods, and ecological restoration and reforestation (Schram and Wampler 2018). Both ecological restoration and widespread reforestation will require changes in the land management, new land-use laws, and enforcement of existing land-use laws.
References
Alscher S (2011) Environmental degradation and migration on Hispaniola Island. Int Migr 49:e164. https://doi.org/10.1111/j.1468-2435.2010.00664.x
Aquagenx LLC (2013) Compartment bag test: instructions for use (2013) https://www.aquagenx.com/wp-content/uploads/2021/06/1-10-Dilution-Instructions-CBT-ECTC-MPN-June2021.pdf. Accessed 2021
Bakalowicz M (2004) The epikarst, the skin of karst. Int J Speleol 37(1):1–10
Balthazard-Accou K, Emmanuel E, Diouf M, Agnamey P (2017) Microbiological contamination of groundwater by Cryptosporidium oocysts in Haiti: health risk assessment for population. Aqua-LAC 9:51–63
Bilham R (2010) Lessons from the Haiti earthquake. Nature 463:878–879
Butler D (2011) No quick fix for Haiti cholera. Nature 478:295–296
Churches CE, Wampler PJ, Sun W, Smith AJ (2014) Evaluation of forest cover estimates for Haiti using supervised classification of Landsat data. Int J Appl Earth Obs Geoinf 30:203–216. https://doi.org/10.1016/j.jag.2014.01.020
CNIGS (2008) Land 98. Haitian National Centre for geospatial information (CNIGS), Port-au-Prince, Haiti. http://www.cnigs.ht/CNIGS/. Accessed March 2022
Cyranoski D (2011) Cholera vaccine plan splits experts. Nature 469:273
Dupuy A (2010) Commentary beyond the earthquake a wake-up call for Haiti. Lat Am Perspect 37:195–204
Dussart-Baptista L, Massei N, Dupont JP, Jouenne T (2003) Transfer of bacteria-contaminated particles in a karst aquifer: evolution of contaminated materials from a sinkhole to a spring. J Hydrol 284:285. https://doi.org/10.1016/j.jhydrol.2003.08.007
Farmer P (2012) Haiti after the earthquake. PublicAffairs, New York, 445 pp
Farmer PE, Ivers LC (2012) Cholera in Haiti: the equity agenda and the future of tropical medicine. Am J Trop Med Hyg 86:7–8. https://doi.org/10.4269/ajtmh.2012.11-0684b
Ford D, Williams PD (2013) Karst hydrogeology and geomorphology. Wiley, Chichester, UK
Gelting R, Bliss K, Patrick M, Lockhart G, Handzel T (2013) Water, sanitation and hygiene in Haiti: past, present, and future. Am J Trop Med Hyg 89:665–670. https://doi.org/10.4269/ajtmh.13-0217
Gerges DI, LaPlant WG, Hyde JN, Previl H, Forrester J (2016) Semi-quantitative estimation of Escherichia coli levels in public drinking water sources in northern Haiti. J Water Sanit Hyg Devel 6:89–95. https://doi.org/10.2166/washdev.2016.043
Ghilardi A, Tarter A, Bailis R (2018) Potential environmental benefits from woodfuel transitions in Haiti: geospatial scenarios to 2027. Environ Res Lett 13:035007
Hadden RL, Minson SG (2010) The geology of Haiti: an annotated bibliography of Haiti’s geology, geography and earth science. US Army Corps of Engineers, Alexandria, VA
Hedges SB, Cohen WB, Timyan J, Yang Z (2018) Haiti’s biodiversity threatened by nearly complete loss of primary forest. Proc Natl Acad Sci 115:11850–11855. https://doi.org/10.1073/pnas.1809753115
Hernandez-Leal PA, Arbelo M, Wilson JS, Diaz AM (2006) Analysis of vegetation patterns in the Hispaniola Island using AVHRR data. Adv Space Res 38:2203. https://doi.org/10.1016/j.asr.2003.06.047
Hwang HG, Kim MS, Shin SM, Hwang CW (2014) Risk assessment of the schmutzdecke of biosand filters: identification of an opportunistic pathogen in schmutzdecke developed by an unsafe water source. Int J Environ Res Public Health 11:2033–2048. https://doi.org/10.3390/ijerph110202033
Jones W (1918) A geological reconnaissance in Haiti: a contribution to Antillean geology. J Geol 26:728
Kambesis PN, Despain J (2019) Karst development on the southwest peninsula of Haiti. GSA Convention, Phoenix, AZ
Kaya GT, Musaoglu N, Ersoy OK (2011) Damage assessment of 2010 Haiti earthquake with post-earthquake satellite image by support vector selection and adaptation. Photogramm Eng Remote Sens 77:1025–1035
Kennedy N, Amacher GS, Alexandre R (2016) Adoption of soil and water conservation practices in central Haiti. J Soil Water Conserv 71:83–90. https://doi.org/10.2489/jswc.71.2.83
Kinzelman JL, Singh A, Ng C, Pond KR, Bagley RC, Gradus S (2005) Use of IDEXX Colilert-18® and Quanti-tray/2000 as a rapid and simple enumeration method for the implementation of recreational water monitoring and notification programs. Lake Reserv Manag 21:73–77
Knowles RB, Markley B, Buckalew JO, Roebuck LW (1999) Report 1999-08. Water resources assessment of Haiti, US Army Corps of Engineers. Mobile District and Topographic Engineering Center, Alexandria, p 93
Koski-Karell V, Farmer PE, Isaac B, Campa EM, Viaud L, Namphy PC, Ternier R, Ivers LC (2016) Haiti’s progress in achieving its 10-year plan to eliminate cholera: hidden sickness cannot be cured. Risk Manag Healthcare Pol 9:14. https://doi.org/10.2147/rmhp.s75919
Lask K, Booker K, Han T, Granderson J, Yang NN, Ceballos C, Gadgil A (2015) Performance comparison of charcoal cookstoves for Haiti: laboratory testing with water boiling and controlled cooking tests. Energy Sustain Dev 26:79–86. https://doi.org/10.1016/j.esd.2015.02.002
Maurrasse FJR (1982) Survey of the geology of Haiti: guide to field excursions in Haiti of the Miami Geological Society, March 3-8, 1982. Miami Geological Society
Mercier de Lépinay B, Deschamps A, Klingelhoefer F, Mazabraud Y, Delouis B, Clouard V, Hello Y, Crozon J, Marcaillou B, Graindorge D (2011) The 2010 Haiti earthquake: a complex fault pattern constrained by seismologic and tectonic observations. Geophys Res Lett 38
Ministère de l’Agriculture (1990) Carte hydrogeologique Republique D’Haiti [Hydrogeological map of the Republic of Haiti]. Port-au-Prince, Haiti. Map no. 3604(E) United Nations, December 1990. Scale 1:250,000
Mukherjee N, Bartelli D, Patra C, Chauhan BV, Dowd SE, Banerjee P (2016) Microbial diversity of source and point-of-use water in rural Haiti: a pyrosequencing-based metagenomic survey. PLoS ONE 11:e0167353. https://doi.org/10.1371/journal.pone.0167353
Periago MR, Frieden TR, Tappero JW, De Cock KM, Aasen B, Andrus JK (2012) Elimination of cholera transmission in Haiti and the Dominican Republic. Lancet 379:E12–E13. https://doi.org/10.1016/s0140-6736(12)60031-2
Phelps MD, Azman AS, Lewnard JA, Antillon M, Simonsen L, Andreasen V, Jensen PKM, Pitzer VE (2017) The importance of thinking beyond the water-supply in cholera epidemics: a historical urban case-study. PLoS Negl Trop Dis 11. https://doi.org/10.1371/journal.pntd.0006103
Piarroux R, Barrais R, Faucher B, Haus R, Piarroux M, Gaudart J, Magloire R, Raoult D (2011) Understanding the cholera epidemic, Haiti. Emerg Infect Dis 17:1161–1168. https://doi.org/10.3201/eid1707.110059
Possee D, Keir D, Harmon N, Rychert C, Rolandone F, Leroy S, Corbeau J, Stuart G, Calais E, Illsley-Kemp F (2019) The tectonics and active faulting of Haiti from seismicity and tomography. Tectonics 38:1138–1155
Rayner J, Murray A, Joseph M, Branz A, Lantagne D (2016) Evaluation of household drinking water filter distribution programs in Haiti. J Water Sanit Hyg Devel 6:42–54. https://doi.org/10.2166/washdev.2016.121
Rebaudet S, Griffiths K, Trazillio M, Lebeau A-G, Abedi AA, Bulit G, Piarroux R, Gaudart J (2017) Cholera spatial-temporal patterns in Gonaives, Haiti: from contributing factors to targeted recommendations. Adv Water Resour 108:377–385. https://doi.org/10.1016/j.advwatres.2016.12.012
Reyes-Ortiz VE, Calderon-Alicea W, Castillo R, Cintron-Garcia JJ, Cruz LC, Hernandez-Munoz A, Irizarry-Perez I, Lockward I, Neste-Laboy C, Ortiz-Leon M, Perez-Homar A, Ramirez-Lopez W, Rivera L, Scholz D, Soto-Ortiz M, Torres-Garcia A (2014) Evaluation of water sanitation health education programme: working with the knowledge of the basic sanitation services in a developing community in rural Haiti after the 2010 earthquake. West Indian Med J 63:616–619. https://doi.org/10.7727/wimj.2013.258
Schram HE, Wampler PJ (2018) Evaluation of hand-dug wells in rural Haiti. Int J Environ Res Public Health 15:1891. https://doi.org/10.3390/ijerph15091891
Shan J, Eguchi R, Jones B (2011) Special issue: Haiti 2010 earthquake foreword. Photogramm Eng Remote Sens 77:995–996
Sheller M, Montalto F, Galada H, Gurian PL, Piasecki M, O’Connor S, Ayalew TB (2014) Participatory engineering for recovery in post-earthquake Haiti. Eng Stud 6:159–190. https://doi.org/10.1080/19378629.2014.964250
Sisson AJ, Wampler PJ, Rediske RR, McNair JN, Frobish DJ (2013a) Long-term field performance of biosand filters in the Artibonite Valley, Haiti. Am J Trop Med Hyg 88(5):862–867
Sisson AJ, Wampler PJ, Rediske RR, Molla AR (2013b) An assessment of long-term biosand filter use and sustainability in the Artibonite Valley near Deschapelles, Haiti. J Water Sanit Hyg Devel 3:51–60
Trček B (2007) How can the epikarst zone influence the karst aquifer hydraulic behaviour? Environ Geol 51:761–765
US EPA (2012) 2012 Recreational water quality criteria documents. EPA 820-F-12-061. Washington, DC. https://beta.epa.gov/sites/default/files/2015-10/documents/rec-factsheet-2012.pdf
Wampler P (2011) Pick sanitation over vaccination in Haiti. Nature 470:175–175. https://doi.org/10.1038/470175a
Wampler PJ, Sisson AJ (2011) Spring flow, bacterial contamination, and water resources in rural Haiti. Environ Earth Sci 62:1619–1628
Wampler PJ, Molla AR, Rediske RR (2016) Transdisciplinary approaches to sustainable water resources and treatment in developing countries. Water Resources IMPACT. https://aquadoc.typepad.com/files/transdisciplinary_approaches_sustainable_water_reso_dcs_wampler-1.pdf. Accessed March 2022
Wampler PJ, Tarter A, Bailis R, Sander K, Sun W (2019) Discussion of forest definitions and tree cover estimates for Haiti. Proc Natl Acad Sci 116:5202. https://doi.org/10.1073/pnas.1901163116
Wang J, Mann P, Stewart RR (2018) Late Holocene structural style and seismicity of highly transpressional faults in southern Haiti. Tectonics 37:3834–3852
Widmer JM, Weppelmann TA, Alam MT, Morrissey BD, Redden E, Rashid MH, Diamond U, Ali A, De Rochars MB, Blackburn JK, Johnson JA, Morris JG (2014) Water-related infrastructure in a region of post-earthquake Haiti: high levels of fecal contamination and need for ongoing monitoring. Am J Trop Med Hyg 91:790–797. https://doi.org/10.4269/ajtmh.14-0165
Woodring WP, Brown JS, Burbank WS (1924) Geology of the Republic of Haiti. Geological Survey of the Republic of Haiti, Port-Au-Prince
Acknowledgements
I would like to acknowledge the help and cooperation of numerous colleagues, among them, Dr. Richard Rediske, Dr. Azizur Molla, Dr. Evens Emmanuel, and others who have contributed to this work. Dawn Johnson and Ellen Bolden at Hôpital Albert Schweitzer Haiti provided valuable insights, access to rural locations, and lab facilities. Numerous students have also contributed their time to assist with fieldwork and research in Haiti, among them Chris Churches, Andrew Sisson, Hayley Schram, and Danielle DeWeerd. I also want to thank James Adamson of Northwater International for providing extensive regional water data in collaboration with Neil Van Dine, Matinot Saintilus, Jean Jackendy, and Brian Jensen of Haiti Outreach. Open access availability of this report was made possible through support from HydroLOGICA.
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Wampler, P.J. Karst aquifers and water resource contamination in Haiti. Hydrogeol J 30, 1453–1467 (2022). https://doi.org/10.1007/s10040-022-02475-8
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DOI: https://doi.org/10.1007/s10040-022-02475-8