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Saddleback Journal of Biology - Saddleback College

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Fall 2009 <strong>Biology</strong> 3B Paper<br />

environments to determine if urban run<strong>of</strong>f can<br />

significantly increase the degree <strong>of</strong> eutrophication. We<br />

hypothesized that rural lakes would have a lower<br />

concentration <strong>of</strong> soluble phosphorous than lakes in<br />

urban environments.<br />

Methods and Materials<br />

Ten 3.5 L water samples were taken from<br />

lakes in California. Five <strong>of</strong> the lakes were chosen from<br />

the Inyo National Forest, near Bishop, CA. These lakes<br />

included Lake Sabrina, Echo Lake, North Lake, TJ<br />

Lake, and Intake #1. The other five samples were<br />

taken from lakes in Orange County, Riverside County,<br />

and San Diego County. These included Laguna Niguel<br />

Lake, Irvine Lake, Lake Elsinore, Mission Viejo Lake,<br />

and Dixon Lake.<br />

Because the relative concentration <strong>of</strong><br />

phosphorous measured was so minute and the risk <strong>of</strong><br />

contamination was so high, care was taken to wash all<br />

glassware with phosphorous free soap. All chemicals<br />

and facilities were provided by the Chemistry<br />

Department at <strong>Saddleback</strong> <strong>College</strong>. The samples were<br />

decanted to remove any solid particles, and then<br />

standardized to 3.00 L. To make the testing and<br />

precipitating <strong>of</strong> phosphate more manageable, all <strong>of</strong> our<br />

samples were boiled down to approximately 40 mL, to<br />

be able to fit into a test tube. A 0.0010 M solution <strong>of</strong><br />

aluminum chloride was prepared and 5 mL were added<br />

to each <strong>of</strong> the samples to form a precipitate. To remove<br />

the possible interference <strong>of</strong> aluminum hydroxide, one<br />

drop <strong>of</strong> 0.100 M nitric acid solution was added to each<br />

<strong>of</strong> the samples. The samples were then centrifuged for<br />

15 minutes and the precipitates were decanted and<br />

washed. The washing and decanting process was<br />

repeated an additional three times to eliminate any<br />

extraneous dissolved ions. The resulting solutions were<br />

then placed into beakers <strong>of</strong> known weight and the<br />

excess water was boiled <strong>of</strong>f. The beakers were<br />

weighed again using an analytical balance, accurate to<br />

10 -4 grams, and the mass <strong>of</strong> the aluminum phosphate<br />

precipitate was determined. Accounting for the<br />

aluminum chloride added and considering that our<br />

original samples were 3.00 L, we converted the mass <strong>of</strong><br />

the precipitate into parts per billion <strong>of</strong> phosphorous.<br />

Results<br />

A one-tailed unpaired t-test was performed<br />

comparing the mean soluble phosphorous<br />

concentration for both urban and rural lake samples.<br />

The test yielded a p-value <strong>of</strong> 1.42x10 -4 , which shows<br />

that the urban lakes sampled had significantly higher<br />

levels <strong>of</strong> soluble phosphorous than the rural lakes<br />

sampled (Figure 1).<br />

Soluble Phosphorous (ppb)<br />

10<br />

90<br />

8<br />

7<br />

6<br />

5<br />

4<br />

3<br />

2<br />

1<br />

0<br />

Urban Lake Location Rural<br />

Lake Location<br />

Figure 1. Mean soluble phosphorous in water samples<br />

from urban and rural lakes. The mean phosphorous<br />

concentration in urban lakes was 82.1589 ± 5.27461<br />

ppb (± SEM, n=5). The mean phosphorous<br />

concentration in rural lakes was 34.6547± 4.62362 ppb<br />

(± SEM, n=5). A one-tailed unpaired t-test revealed a<br />

significant difference between the phosphorous<br />

concentration in rural and urban lakes (P=1.42x10 -4 ).<br />

Figure 2. Carlson’s Trophic State Index which<br />

describes the degree <strong>of</strong> eutrophication in a lake based<br />

on the amount <strong>of</strong> total phosphorous in parts per billion.<br />

Discussion<br />

For further analysis <strong>of</strong> the eutrophication<br />

problem, the trophic state <strong>of</strong> the lakes was compared<br />

using The Carlson Trophic State Index (Figure 2). The<br />

mean phosphorous concentration <strong>of</strong> urban lakes, 82.16<br />

ppb, fell into the hypereutrophic zone. This rating<br />

describes a lake with excessive algal blooms, which<br />

has reduced oxygen content at lower depths and dead<br />

zones beneath the surface (Boesch et al., 2001). The<br />

rural lakes’ mean phosphorous concentration was 34.65<br />

ppb, falling into the mesotrophic to slightly eutrophic<br />

zone. Lakes in this classification are productive and<br />

support a regularly functioning ecosystem with a<br />

healthy balance between the primary producers and<br />

consumers.<br />

Our experiment also points to the possible<br />

efficacy <strong>of</strong> using aluminum to remove phosphate from<br />

a body <strong>of</strong> water. Our precipitate was obtained using<br />

very minute amounts <strong>of</strong> reagents and a slightly acidic<br />

solution, which mimics the natural condition <strong>of</strong> most<br />

lakes (Smith et al. 2001) Because aluminum phosphate<br />

127<br />

<strong>Saddleback</strong> <strong>Journal</strong> <strong>of</strong> <strong>Biology</strong><br />

Spring 2010

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