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I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br /> I <br /> I <br /> I <br /> I <br /> I <br /> I <br /> I <br /> I <br /> <br />13 <br /> <br />Nevertheless, some ecosystems are irreplaceable once destroyed. For example, <br />the loss of a mature stand of maple-basswood forest is not easily restored <br />within a short period of time'. The mature maple-basswood forest is a unique <br />ecosystem in Minnesota and its loss could not be replaced by other tree stands. <br /> <br />Another potential problem when replanting vegetation at a landfill site after <br />closure is maintaining the integrity of the landfill cover.~ Because water <br />should be prevented from entering the landfill, plants with deep roots should <br />be avoided. This limits the types of crops or grasses that can be grown when a <br />landfill area is covered. <br /> <br />If wetlands are part of the waste facility's acreage, they should be located in <br />the buffer zones. If a protected wetland is destroyed, another of greater or <br />equal value should be constructed within the facility boundaries or elsewhere. <br />State law does allow the "trading" or substitution of wetlands with the con- <br />currence of the Minnesota Department of Natural Resources (DNR). <br /> <br />The PCA requires that completely filled areas of a landfill be covered with <br />adequate topsoils and seeded to prevent erosion. PCA must approve a develop- <br />ment plan for the site and immediately adjacent areas, including plans for the <br />site's end use. PCA's responsibility for a site ends once the permit condi- <br />tions for closing a facility have been satisfactorily met. <br /> <br />Replacement of vegetation lost during development and operation of a sanitary <br />landfill should be the responsibility of a landfill operator. A facility plan <br />specifying such conditions could be.negotiated between the community and the <br />developer, with the advice of the DNR. <br /> <br />When wetlands are traded or reestablished, the developer should negotiate <br />alternative or replacement wetland sizes and locations with the community and <br />DNR. Trading of wetlands and the preparation of plans to replace vegetation <br />should be conducted concurrently with the permit review process to ensure no <br />measures are made that conflict with environmental protection measures required <br />by the PCA. <br /> <br />POTENTIAL HEALTH RISKS <br /> <br />Operation of waste disposal facilities can pose potential health related prob- <br />lems: 1) Contamination of well water by leachate from landfills may endanger <br />the health of animals and humans consuming the water; 2) landfills may be the <br />source of diseases carried by insects and rodents; and 3) landfills may be the <br />site of accidents such as waste spills, fires or explosions. <br /> <br />Measures are available to guard against these risks, but the potential for risk <br />cannot be completely eliminated. For example, no mitigating measure will com- <br />pletely eliminate the health risk resulting from groundwater contamination <br />(discussed later in the section on compensation). <br /> <br />The potential health risks associated with transmission of disease by insects <br />and rodents have been reduced significantly in the last decade since the prac- <br />tice of open dumping was prohibited. Generally, the potential for diseases <br />from such exists only while the facility is operating. <br /> <br /> <br />