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system and providing examples of the consequences of its inadequate implementation. From the review, it is clear that there is a strong linkage between poor SWM and environmentalhealth issues. The rapid increase in population, economic growth, urbanization and industrialization improve the generation of SW at global level, boosting environmental contamination when such SW is not managed. Indeed, in many developing countries waste is scattered in urban centers or disposed of in open dump sites. The lack of infrastructure for collection, transportation, treatment and final disposal, management planning, financial resources, know-how and public attitude reduces the chances of improvement, as pointed out also by other authors . In Table 4 the main source of contamination and health risks due to SW mismanagement for each waste stream are summed up. State compliance is monitored by EPA inspections. In the case that waste management guideline standards are not met, action against the sitewhich? will be taken. Compliance errors may be corrected by enforced cleanup directly by the site responsible for the waste or by a third party hired by that site. Prior to the enactment of the Clean Water Act and RCRA, open dumping or releasing wastewater into nearby bodies of water were common waste disposal methods. The negative effects on human health and environmental health led to the need for such regulations. The RCRA framework provides specified subsections defining nonhazardous and hazardous waste materials and how each should be properly managed and disposed of. Guidelines for the disposal of nonhazardous solid waste includes the banning of open dumping. Hazardous waste is monitored in a “cradle to grave” fashion; each step in the process of waste generation, transport and disposal is tracked. The EPA nowwhen? manages 96 million tons of solid, hazardous and industrial waste. Since establishment, the RCRA program has undergone reforms as inefficiencies arise and as waste management processes evolve. marine ecosystem. An environmental assessment and literature survey were conducted to characterize the coastal marine pollution impacts caused by human-made activities. The assessment revealed that municipal waste incineration of organic waste and plastics in open dump areas is a potential source of unintentionally produced persistent organic pollutants such as dioxins and furans. Plastic is one of the most abundant solid wastes at sea and shorelines, representing 25 % of the total marine debris. More than 50 % of current-use pesticides applied in the agriculture zone of the inhabited islands were identified as endocrine-disrupting chemicals, underlying potential health effects in the endemic fauna. Oil spills and traces of hydrocarbons threaten the long-term survival of marine species due to the current reliance on fuel transported from Ecuador’s mainland coast. Concerted local

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