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------=_NextPart_01C5A711.CF57AF40 Content-Location: file:///C:/E72B5D12/FeliciePoster_files/pres.xml Content-Transfer-Encoding: quoted-printable Content-Type: text/xml; charset="utf-8" ------=_NextPart_01C5A711.CF57AF40 Content-Location: file:///C:/E72B5D12/FeliciePoster_files/slide0002.htm Content-Transfer-Encoding: quoted-printable Content-Type: text/html; charset="us-ascii" Chlorine and Selenastrum Population Growth
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Effects of Chlorine on Population Growth of Selenastrum capricornutum
Felicie Reid, Dr. Ann Throckmorton, and Dr. Helen Boylan, Department= s of Biology and Chemistry, Westminster College, PA
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Introduction= 3;
     Chlorine is a co= mmonly used disinfectant in drinking water.  It is effective at removing odors and harmful microorganisms = and in reducing the formation of biofilms in water pipes.  Chlorination is used <= /span>in wastewater treatment plants, eventually being released into the environment thro= ugh effluent pipes.  Chlorine may= have negative effects on both humans and wildlife.  It reacts with organic and inorganic matter= in the source water to form disinfection byproducts.  This can be leth= al to fish and can disrupt the structure of natural communities.  In the 1996 Safe Water Drinking A= ct, the EPA set the maximum limit for chlorine in drinking water at 4 mg/L.=
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= Figure 1.  Microscopic photograph of= Selenastrum = capricornutu= m  
   &nbs= p; = Selenastrum capricornutum is a unicellular alga commonly used in toxicological studies.  We sought to assess= the potential impact of chlorine on the environment through a laboratory toxici= ty test with this algal species.
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Conclusions
     This study has = shown that chlorine in concentrations found in natural waterway= s can adversely affect populations of algae, and that chlorine from wastewater treatment plant effluents may have detrimental effe= cts on aquatic organisms.  As chlori= ne concentrations increase, the growth of algal populations is suppressed.  At high chlorine concentrations, population size decreases.  Thus, chlorine may affect not only = algal populations, it also has the potential to disrupt the structure of ent= ire aquatic ecosystems.
     Various related studies have been conducted to determine the effects of chlorine on n= atural ecosystems.  Urban lakes in t= he Phoenix metropolitan area were tested for free and total chlorine.  Tests showed <= /span>that phytoplankt= on abundance and biomass decreased with increasing chlorine concentrations.  Phytoplankton genera were differentially affected by the chlorine concentratio= ns (Hunter, et al., 1999).  Also= , researchers at t= he Woods Hole Oceanographic Institution found that free chlorine concentrations ranging from 0.02 to 0.03 mg/L had no significant adve= rse effects on phytoplankton.  Ho= wever, levels of 0.03 to 0.13 mg/L reduced phytoplankton growth, and levels above 0.13 mg/L caused a complete washout of organisms (Goldman and Davidson, 1977).  A = study at the University of Massachusetts showed that chloride = dioxide in concentrations of 1,3, and 5 mg/L have adverse effects on microalgal cultu= res (Sukenik, et al., 1987).
     Despite the pot= ential for negative effects, there are benefits to chlorination = 211; it eliminates odors and reduces risk of waterborne diseases.  However, chlorination may have detrimental effects on the ecosystems that receive treated water.  Further analysis must= be done to determine whether beneficial effects of chlorination counterbalance possible detrimental effects on aquatic ecosystems and = the organisms that live there.
     Methods    
     Water samples w= ere taken near the outflow from the effluent pipe of a wastewater treatment plant along the Little Neshannock Creek in western Pennsylvania.  Samples were collected daily over an eight-day period and the concentration of total chlorine was determined.  The chlorine concentrations ranged from 0.25 mg/L to 0.97 mg/L, with an average of  0.65 mg/L.  The instrument used for chlorine analysis was a Hach DR/820 portable colorimeter. 
     A series of dis= hes were set up with 50 mL of solution and 1 mL of Selenastrum = culture in each.  The control group had = no added chlorine.  <= /span>One treatment h= ad a chlorine concentration of 0.33 mg/L, while the other had 0.66 mg/L.  There were 12 replicat= es of each treatment.  The dishes were set onto light tables with a photoperiod of 18 hours of daylight and ei= ght hours of darkness.  Cell coun= ts were conducted every two days with a hemocytometer.  The data were analyzed using a on= e-way Analysis of Variance followed by Tukey’s Honestly Significant = Difference Test= .
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= Figure 3.  Difference in average cell numbers on the final day of the experiment at three concentrations of chlo= rine
Figure 4.  Analysis  of final population size of Selenastrum cultures in three treatment groups.  The p-value is m= uch less than 0.05, indicating a very significant difference between treatment= s.
Figure 5.   Population size of Selenastrum in three chlorine concentrations.  At increased chlorine = concentrations, = the population growth of Selenastrum was suppressed.  At 0.33 mg/L, the algae showed logistic growth,= while at 0.66 mg/L of chlorine, Selenastrum populations eventually declined.
Results
     Statistical ana= lyses showed a significant difference between the three treatments.  Non-chlorine cultures showed the greatest algal growth, while increasing chlorine concentrati= ons resulted in decreasing Selenastrum population growth.  Thus, we can conclud= e that the concentration of chlorine from wastewater treatment pla= nt effluents along the Little Neshannock Creek is sufficient to adversely affect algae in local aquatic communities. 
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= Figure 2.  The population size of Selenastrum on the final da= y of cell counts.
Literature Cited
     Goldman, J.C. a= nd J.A. Davidson.  1977.  Physical model of marine phytoplankton chlorination at coastal power plants.&nbs= p; Environmental Science and Technology 11(9):908-913.
     Jennifer A. Hun= ter, Mark Compton, and Milton R. Sommerfeld.&n= bsp; 1999.  Eff= ects of chlorine gradient on algal diversity and biomass in an urban lake.  Arizona State University Undergra= duate Research Poster Symposium.
     Sukenik, A., et al.  1987  Effects of oxidants on microalgal= flocculation.  Proceedings AWWA Annual Conference.  =
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