Laserfiche WebLink
�gsftk�'g;answers cumulatll a a ist we sffa first <br />subscribers T s feat re wil fle g ailgE = arse!ectE <br />tin hi raet ceatannowic cj;times;A erea Ef onlh <br />s closed, the nswers.wi(l ( sa yeti c r an=o lines:arc <br />hroAghtheA'PA;ZoningPracticewebzpages Y <br />to find a wide range of necessary resources. <br />Assessment involves establishing baseline <br />conditions, impacts, alternatives, and mitiga- <br />tion for the proposed action in order to report <br />and evaluate the likely health outcomes —such <br />as unnecessary exposure to air pollution and <br />particulate matter —and their effects, such as <br />increased respiratory disease and asthma, on <br />the targeted population(s). Assessing the avail- <br />able information, research, and resources will <br />allow HIA practitioners to evaluate risks and <br />benefits in light of the specific details of the <br />individual HIA. The assessment should also <br />clearly identify who may be affected and how <br />they will be affected. <br />During the reporting phase, the find- <br />ings from the HIA should be developed in <br />such a way so as to facilitate health -based <br />recommendations to aid the decision -mak- <br />ing process with respect to the proposed <br />action. Recommendations should also <br />include a viable plan for implementation. <br />Involvement and input from the various <br />stakeholders in the process is crucial. Fi- <br />nally, the monitoring phase allows for con- <br />tinuing evaluation by engaged stakeholders <br />and others in order to track the outcomes of <br />a decision and its implementation. <br />HISTORY AND GROWTH OF HIA USE <br />HIA in the U.S. evolved from ElAs required <br />by the National Environmental Policy Act of <br />1969 (NEPA) or state -enacted "mini-NEPAs" <br />in response to the need for a more inter- <br />disciplinary approach to health inequities. <br />Historically, ElAs were criticized for failing <br />to take into consideration the effects of <br />projects on health generally, rather than <br />evaluating only toxic exposures and sources <br />of biophysical concerns unrelated to a "com- <br />.associate`ed <br />terra Alban' <br />3eComm ttE <br />udean a <br />prehensive and systematic approach to hu- <br />man health impacts" (Bhatia and Wernham <br />zoo8). However, by the late 198os, the <br />term "environment" grew to include social, <br />cultural, and human health considerations, <br />which in turn led to the growth of interest in <br />the health outcomes of development proj- <br />ects and other land -use decisions. In 1999, <br />the World Health Organization produced the <br />Gothenburg Consensus Paper, which intro- <br />duced and clearly outlined the concept of <br />HIA and eventually led to the development <br />and implementation of HIA as a method for <br />evaluating the potential effects of changes <br />to the built environment. <br />Today, HIAs may be linked to ElAs or <br />they may be conducted as independent <br />processes. While ElAs do occasionally <br />include health risk assessments, and the <br />U.S. Environmental Protection Agency does <br />conduct formal health -effects forecasting <br />as part of legally mandated cost -benefit <br />analyses, HIAs are not routinely required or <br />performed in any setting in the U.S. More- <br />over, as contrasted with EIA preparation by <br />engineers and land -use or environmental <br />consulting firms, HIA preparation is typically <br />performed by public health professionals. <br />The use of HIA, therefore, has relied on vol- <br />untary inclusion of such assessment into the <br />development projector plan, rather than the <br />required processes of EIA under NEPA. <br />HIA vs. EIA <br />Discussions surrounding the potential bene- <br />fits from the increased use of HIA have raised <br />questions about whether such assessments <br />can, and should, be mandatory and whether <br />the means are available for incorporating HIA <br />into existing legislative, regulatory, or admin- <br />istrative procedures (Ko zo11). While some <br />proponents agree that conducting an HIA <br />during the course of a required EIA could save <br />time and money, others are concerned that <br />the inclusion of an HIA into an EIA will dimin- <br />ish the importance and relevance of the pub- <br />lic health issues and could lead to legal chal- <br />lenges. Opponents of HIA have also argued <br />i:A health impact assessment; <br />ofthis'-stretch ofth e Buford <br />j lighwayinAtlanta evaluated <br />the health effects <br />redeveloping the roadwayto <br />reduce the number of lanes <br />add sidewalks, crosswalks;;;,;_; <br />and on:streetparkirig, all` <br />with -the goal'of makingthe <br />area less dangerous for <br />people bit 4fo ot. orbike: <br />ZONINGPRACTICE io.ai <br />AMERICAN PLANNING ASSOCIATION J page 3 <br />