Chromium Discussion

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    Results

    Absorbance band, max = 435nm

    Table 1: Concentration and absorbance of standard solution

    Concentration

    (ppm)Absorbance

    0 0.002

    18.75 0.127

    37.5 0.283

    75 0.469

    150 0.844

    Table 2: The absorbance band of simulated lake water

    Water sample

    Absorbance

    0.275

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    Fig 3.1: Graph of absorbance versus concentration

    Calculation

    Standard Solution Calculation

    Standard solution = 18.75 ppm

    M1V1 = M2V2

    V1 = (M2V2) / M1

    V1 = (18.75 ppm x 50mL) / 300 ppm

    = 3.125 mL

    Standard solution = 37.5 ppm

    M1V1 = M2V2

    V1 = (M2V2) / M1

    V1 = (37.5 ppm x 50mL) / 300 ppm

    = 6.25 mL

    y = 0.0055x + 0.0341

    R = 0.9916

    0

    0.1

    0.2

    0.3

    0.4

    0.5

    0.6

    0.7

    0.8

    0.9

    1

    0 20 40 60 80 100 120 140 160

    Absorbance

    Concentration (ppm)

    Graph of Absorbance Versus Concentration

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    Standard solution = 75 ppm

    M1V1 = M2V2

    V1 = (M2V2) / M1

    V1 = (75 ppm x 50mL) / 300 ppm

    = 12.5 mL

    Standard solution = 150 ppm

    M1V1 = M2V2

    V1 = (M2V2) / M1

    V1 = (150 ppm x 50mL) / 300 ppm

    = 25 mL

    Y = 0.005x + 0.034

    (0.275) = 0.005x + 0.034

    X = (0.275 0.005) / 0.034

    = 7.94 ppm

    Notice that x is equivalent to the concentration of Chromium (VI) contains in the water

    sample, which is 7.94 parts per million (ppm).

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    Discussion

    Many heavy metals, including chromium (Cr), are toxic even at low aqueous solution

    concentration. Chromium ions, Cr (III) and Cr (IV) are found naturally in rivers, lakes and

    streams. The main objective of this experiment is to determine the quantity of Cr (IV)present in a polluted water sample using a spectrophotometer and a set of standard

    solutions. Besides, this experiment was performed to evaluate the suitability of the lake

    water for public consumption. This experiment was analyzed by using the

    spectrophotometer with wavelength 435 nm. Distilled water was used as the sample in

    order to calibrate the spectrophotometer. Beer-Lambert Law states that absorbance

    value depends on the total quantity of the absorbing compound in the light path through

    the specific wavelength of the sample.

    Five dilution of Cr (VI) standard solution has been prepared at concentration of

    0ppm, 18.75ppm, 37.5ppm, 75ppm, and 150ppm from 300ppm of stock solution. The

    result shows that the absorbance for each concentration of Cr (VI) has different value of

    absorbance. As the concentration increased, the absorbance value is also increased.

    From the results obtained, it shows that at blank sample, absorbance value was at

    0.002, but at concentration of 150.00ppm, absorbance value was increases to the

    highest values which are at 0.844. The absorbance values at the concentration of

    18.75ppm, 37.5ppm, and 75ppm were 0.127, 0.283, and 0.469 respectively. This result

    proved that the absorbance of a solution is directly proportional to the concentration of

    the solution and this condition follows the rules of Beers Law.

    After the graph of absorbance versus concentration of Cr (VI) has been plotted,

    an equation of Y = 0.005x + 0.034 was obtained from the graph. R 2 from the graph

    shows the value at 0.991 which is approximately to 1. The closer the R2value is to 1.00,the better the linear regression analysis fits the data. Then, the Y = 0.005x + 0.034

    equation can be used to determine the concentration of chromium in the sample lake

    water. The absorbance of lake water sample was at 0.275. By applying this equation, the

    concentration of sample lake water was 7.94ppm.

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    According to the values of concentration of chromium (VI) which is apparently

    calculated to contain 7.94 parts per million, this obviously means that there is a

    significant content of chromium ions in the water. Based on the consideration of state

    and federal regulatory agencies, natural waters are regarded to be toxic if the

    concentration of Chromium (VI) is any higher than 0.100 parts per million. The presence

    of chromium (VI) even in very low concentration is highly visible and causes damage to

    the environment as they are toxic to aquatic life (I.U Emmamuel et al., 2009). The impact

    Cr (VI) exposure to water bodies can cause allergy reactions, dermatitis, skin irritation,

    cancer and mutation both in babies (Garg et al., 2003). The lake water sample tested is

    then concluded to be unsafe and unhealthy for drinking water for public consumption or

    even agricultural purposes.

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    Conclusion

    The main purpose of this experiment is to determine the quantity of Cr (IV) present in a

    polluted water sample using a spectrophotometer and by using a set of standard

    solutions of known concentration. In this experiment, absorption spectroscopy will beused to determine Cr (VI) concentrations in solution with specific wavelength of 435 nm.

    Chromium is a component in automobile brakes and engine parts. Chromium

    deposited on highways, in the form of brake dust and engine exhaust, can leak into

    lakes and streams via rainwater run-off. Lakes and streams near highly trafficked areas

    are highly susceptible to chromium contamination.

    The concentration of chromium (VI) in the lake sample tested is 7.94 ppm. At this

    concentration of Cr (VI), it can cause the water pollution. The lake water can be very

    toxic especially to aquatic life and human being. Result of this experiment shows that the

    concentration of Cr (VI) is over the limit for drinking water or for agricultural purposes. At

    this concentration level, the water sample could specified as toxic and prolonged

    contact with some chromium compounds that can cause allergy reactions, dermatitis,

    skin irritation, cancer and mutation both in babies. Since it is highest than 0.100 ppm that

    been standardized by state and federal regulatory agencies, the water sample is

    concluded to be contaminated and thus not suitable for drinking and agricultural

    purpose.