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The Ohio Journal of - The Ohio Academy of Science

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A-42 <strong>The</strong> <strong>Ohio</strong> <strong>Journal</strong> <strong>of</strong> <strong>Science</strong><br />

Vol. 112(1)<br />

1nM solutions produced a limited growth with only 143%<br />

and 147% increases, respectively. <strong>The</strong>se results imply<br />

that diatoms can react to small amounts <strong>of</strong> iron in their<br />

environment and the optimal concentration to remove the<br />

most carbon dioxide from the atmosphere was around 5<br />

nM. <strong>The</strong>se findings suggest that iron fertilization may be<br />

adopted as a carbon sequestration strategy.<br />

Poster Board No. 026 THE EFFECTIVENESS OF THE SOLAR<br />

DISINFECTION METHOD (SODIS) IN TREATING CONTAMINATED<br />

WATER. Osama Alkhalili, osamaalkhalili8@yahoo.com, 4691<br />

Fairway Lane, Sylvania <strong>Ohio</strong> 43560 (Maumee Valley Country<br />

Day School).<br />

<strong>The</strong> lack <strong>of</strong> access to safe drinking water in undeveloped<br />

nations demands finding affordable water-disinfection<br />

methods. This project investigates the effectiveness<br />

<strong>of</strong> the solar disinfection method (SODIS) in treating<br />

contaminated water. It is hypothesized that exposing<br />

contaminated water to sunlight for a specific time will<br />

be effective in disinfecting the contaminated water. All<br />

tools were sterilized by boiling prior to collecting a water<br />

sample from Lake Olander in Sylvania, <strong>Ohio</strong>. Two clean<br />

16-oz PET plastic bottles were filled with the lake water,<br />

placed onto a dark, metal sheet beneath a lamp with a<br />

Daylight Blue Reptile bulb and exposed to UV-A light at<br />

350 nm for 12 and 24 hours, respectively. A third PET<br />

bottle was filled with filtered lake water using a Whitman<br />

Filter Paper and exposed to UV-A light for 24 hours. One<br />

cup <strong>of</strong> the lake water was boiled for 15 minutes. Samples<br />

were cultured on tryptic soy agar plates. Bacterial colonies<br />

in each plate were counted after 24, 48, 72, and 96 hours.<br />

<strong>The</strong> entire experiment was repeated two additional times.<br />

In the untreated sample, the average numbers <strong>of</strong> bacterial<br />

colonies were 95, 170, 320, and 500 at 24, 48, 72, and 96<br />

hours, respectively. Boiled sample showed no bacterial<br />

growth over the 96-hour period. <strong>The</strong> 12-hour SODIS sample<br />

resulted in an average bacterial growth <strong>of</strong> 30, 45, 75 and<br />

130 colonies at 24, 36, 48 and 96 hours, respectively. <strong>The</strong><br />

unfiltered 24-hour SODIS sample resulted in an average<br />

bacterial growth <strong>of</strong> 5, 8, 12, and 22 colonies at 24, 48,<br />

72, and 96 hours, respectively, while the filtered 24-hour<br />

sample had 2, 4,7, and 12 colonies at 24, 48, 72, and 96<br />

hours, respectively. Results showed that boiling is the most<br />

effective method for disinfecting contaminated water. <strong>The</strong><br />

SODIS method could be fairly effective, if optimal exposure<br />

time is used. <strong>The</strong> turbidity <strong>of</strong> the water may reduce the<br />

efficiency <strong>of</strong> the SODIS method, which can be corrected<br />

easily by water filtration. <strong>The</strong>se findings suggest that the<br />

SODIS can be adopted as a water-disinfection method<br />

in undeveloped nations that do not have the means and<br />

infrastructures to clean and disinfect their drinking water.<br />

Poster Board No. 027 THE EFFECTS OF GREEN MATERIALS<br />

UTILIzED AS ABSORBENTS IN OIL SPILL CLEAN UP. Hannah A.<br />

Barlow, mbarlow25@yahoo.com, 7245 zwickle Rd., Logan OH<br />

43138. (Logan-Hocking Middle School)<br />

This project began out <strong>of</strong> concern over the 2010 Gulf<br />

<strong>of</strong> Mexico oil spill cleanup efforts, to determine which<br />

materials would best absorb oil. It was hypothesized that<br />

“green” materials could be used to effectively absorb oil.<br />

Materials used were 1.5 cattail seed heads, 2 corn cobs, 4<br />

pine cones (Spruce), and 1 cup (227kg) Lake Huron zebra<br />

mussel shells. <strong>The</strong>se “green” materials were crushed to<br />

measure one-half cup (113kg), and then placed into each<br />

<strong>of</strong> the one cup (227kg) capacity funnels with 6 ½ inch<br />

(16.5cm) necks. Next, one-half cup (118ml) <strong>of</strong> used motor<br />

oil was poured into each <strong>of</strong> the funnels to drain into one<br />

cup (250ml) glass beakers. Cattail seed heads absorbed 2.5<br />

oz. (75ml) <strong>of</strong> oil or approximately 60%. Corn cobs absorbed<br />

2.02 oz. (60 ml) <strong>of</strong> oil or approximately 50%. Pine cones<br />

absorbed .51 oz. (15ml) or approximately 13%. Zebra<br />

mussel shells absorbed .34oz. (10ml) or approximately<br />

less than 1%. <strong>The</strong>se results indicate that it would take<br />

approximately 3 cattails to absorb one cup (236ml) <strong>of</strong> oil.<br />

Based on 16 cups (3784ml) per 1 gallon, it would take 48<br />

cattails to absorb one gallon <strong>of</strong> oil, and therefore 2,016<br />

cattails per barrel <strong>of</strong> oil based on a 42 gallon barrel. Since<br />

60,000 barrels <strong>of</strong> oil were leaked daily during the 2010 Gulf<br />

oil spill, it would take approximately 120,960,000 cattails<br />

to absorb one days worth <strong>of</strong> oil from the Gulf oil spill, or<br />

11,007,360,000 cattails to absorb the 91 days worth <strong>of</strong> oil<br />

spilled into the Gulf <strong>of</strong> Mexico. This research demonstrates<br />

that green technology could be considered and used as an<br />

environmentally sound solution for future oil spills.<br />

Schar Room 266<br />

Poster Board No. 033 AQUATIC OIL SPILL CLEAN-UP. Abigail<br />

L Myers, myersa13@embarqmail.com, 4251 N County Line<br />

Rd, Sunbury, OH 43074 (Big Walnut Middle School)<br />

Oil produced <strong>of</strong>fshore to meet energy needs is transported<br />

through aquatic environments. In <strong>of</strong>fshore drilling and<br />

production (e.g., BP Deepwater Horizon) and oil transport<br />

(e.g., Exxon Valdez), accidental spills occur. <strong>The</strong>refore,<br />

cleaning up spills is necessary – one method is to use<br />

sorbents. For a sorbent to be successful in an aquatic<br />

environment, it must have a high level <strong>of</strong> oleophilicity and<br />

be hydrophobic. Absorption and adsorption are processes<br />

that can remove oil from water. Through absorption, oil fills<br />

in cavities in the sorbent and through adsorption oil sticks<br />

to the material surface. This experiment investigated how<br />

well synthetic (polypropylene, polyurethane, and polyester)<br />

and organic (cotton, straw, and sawdust) sorbents remove<br />

oil from water by absorption and/or adsorption. Initial<br />

research led to the hypothesis: synthetic sorbents would<br />

remove more oil than natural organic sorbents, with<br />

polypropylene being the best. Each sorbent (1.5g) was<br />

placed into a beaker containing an oil slick (20 ml) floating<br />

on the water surface (150 ml), timed (5 min), and removed.<br />

<strong>The</strong> masses <strong>of</strong> used sorbent and fluids were determined,<br />

and volumes <strong>of</strong> remaining fluids were measured. <strong>The</strong><br />

synthetic sorbents demonstrated greater effectiveness than<br />

natural organic sorbents, with a mean weight ratio (mass<br />

<strong>of</strong> oil removed to mass <strong>of</strong> sorbent used) <strong>of</strong> 9.5, compared<br />

to 7.9 for organic sorbents. Based on this experiment,<br />

polyester removed the most oil, with a weight ratio <strong>of</strong> 13.5,<br />

followed by cotton (12.2), polypropylene (9.4), sawdust<br />

(6.6), polyurethane (5.5) and straw (4.9). Additional work<br />

could include revised methods to simulate wave action.<br />

Poster Board No. 034 LEAD CONTENT OF SCHOOL DRINKING<br />

WATER. Halle A. Miller, millerbdhc@aol.com, 13684 Janell<br />

Drive, Columbia Station OH 44028 (Columbia High School)<br />

<strong>The</strong> goal <strong>of</strong> this project was to discover how the lead content<br />

<strong>of</strong> drinking water varied between school buildings <strong>of</strong><br />

different ages. <strong>The</strong> objective was to determine if there was<br />

a direct correlation between school age and the lead content<br />

<strong>of</strong> its drinking water. <strong>The</strong> hypothesis was that if a school is<br />

older, the lead content <strong>of</strong> the drinking water will be greater<br />

because <strong>of</strong> different piping and soldering methods used in<br />

the past. Three water samples were collected from each <strong>of</strong><br />

ten different public high schools from a restroom sink. Each<br />

sample was collected from a faucet running cold water and<br />

the test tubes were sealed with Parafilm. A stopwatch was<br />

used to time thirty seconds between samples. <strong>The</strong> samples<br />

were tested at the Avon Lake Water Filtration Plant, with<br />

help from a qualified scientist, using the graphite furnace<br />

<strong>of</strong> an Atomic-Absorption Spectrometer. Standard samples<br />

were analyzed for calibration and then conducted on Test<br />

Group #1. A blank sample was run to recalibrate the<br />

machine and the process was repeated for Test Group #2<br />

and then Test Group #3. <strong>The</strong> standard deviation results in<br />

parts per billion (site one 2.68ppb, site two 0.40ppb, site<br />

three 0.35ppb, site four 0.91ppb, site five 9.45ppb, site six<br />

0.38 ppb, site seven 9.45ppb, site eight 0.68ppb, site nine<br />

0.17ppb, site ten 0.69ppb), were under the EPA specified<br />

15ppb. However, some <strong>of</strong> the raw samples reached levels<br />

<strong>of</strong> 20.0ppb and 25.3ppb. <strong>The</strong> results were found to support<br />

the hypothesis, on average. <strong>The</strong> schools built before 1967<br />

had greater lead contents, on average, and the schools<br />

built during or after 1967 had little to no lead detected in

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