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Last modified
7/28/2009 2:38:58 PM
Creation date
4/18/2008 9:59:11 AM
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Weather Modification
Title
Currents…Developing Technology for Tomorrow's Challenges
Date
1/1/1993
Weather Modification - Doc Type
Report
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<br />Humans have used other living organ- <br />isms for many years to monitor life support <br />systems. One of the best known examples, <br />the caged canary in the mine, served as an <br />advance warning of trouble to miners. An <br /> <br />11 <br /> <br />Bioassays, using single species test or- <br />ganisms, are also used to detect effects of <br />toxicants which may exist in the water. <br />Standard toxicity test methodologies exist <br />for Daphnids (water fleas) such as <br /> <br />Biosurveys and <br />Bioassays - <br />Sentinels of the <br />Environment <br /> <br />S. MARK NELSON and RICHARD A. ROLlNE <br />Applied Sciences Branch <br /> <br />extreme sensitivity to toxic gases caused <br />the canary to experience distress sooner <br />than its human companions. <br />Reclamation presently uses biological <br />data in much the same way to monitor con- <br />ditions in some of its water resources. <br />Biomonitoring of waters can include both <br />field and laboratory studies-biosurveys <br />and bioassays. During a biosurvey, organ- <br />isms are collected (usually aquatic macro- <br />invertebrates, but sometimes fishes) from <br />the environment. Analyzing these biologi- <br />cal communities allows for detection of <br />environmental impairment. Recent devel- <br />opments by the EP A (Environmental <br />Protection Agency) in this area have <br />allowed for greater ease in the presentation <br />of these types of data. Rather than report a <br />confusing list of scientific names, new <br />techniques now summarize this informa- <br />tion into a single number which cor- <br />responds to a stream condition. <br /> <br />C eriodaphnia dubia and the fathead min- <br />now Pimephales promelas. Test end points <br />range from mortality in acute tests <br />(~ days in length) to number of young <br />produced and growth in chronic tests <br />(>4 days in length). <br />Biosurveys and bioassays are used to <br />detect impairment and toxicity, respec- <br />tively. They do not, however, provide <br />direct information on the cause of impair- <br />ment or toxicity. This additional infor- <br />mation requires physical habitat measure- <br />ments and chemical sampling. In the case <br />of toxicants, chemical sampling cannot be <br />relied on solely because only living organ- <br />isms integrate the dynamics of the <br />chemical, physical, and biological world <br />that they inhabit. In many cases in the past, <br />chemical water quality standards have <br />underprotected the environment. This <br />underprotection occurred because the <br />standards did not account for the effects of <br />combinations of toxicants or the effects of <br />the environment (e.g., pH, buffering capac- <br />ity, and dissolved oxygen shifts) on the <br />toxicants. <br />
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