Laboratory 7– CE 321, Fall 2013

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Laboratory 7– CE 321, Fall 2013

Geochemistry Assessment of the Bushkill Creek Watershed

You may work in groups of three.

Objectives

Measure the alkalinity of a number of samples from the Bushkill Stream and a standardized sample.

Gain an understanding of the natural buffer system.

Introduction

In this lab you will perform alkalinity titration on a various samples from the Bushkill

Stream. You will combine all of the class information and then relate the difference in the sample results to the geology of the Bushkill Stream watershed, and its ability to buffer acid precipitation.

Background

Alkalinity is defined in a number of ways; in general alkalinity is a measurement of the capacity of water to accept protons. Alkalinity is also defined as the sum of all titratable bases down to a pH of 4.5; the titratable limit is found by determining how much acid it takes to lower the pH of water to 4.5. One other common way to define alkalinity is the capacity of water to neutralize strong acid; every body of water has an “acid neutralizing capacity” (ANC).

In most natural waters the only significant contribution to alkalinity are the carbonate species and any free H

+

or OH

-

. For practical purposes Alkalinity is defined as:

Alkalinity (mole/L) =

HCO

3

 

CO

3

2

 

OH

 or

Alkalinity (eq/L) = ( HCO

3

)

( CO

3

2

)

( OH

)

The more rigorous definition is as follows:

Alkalinity, mole/L =

HCO

3

 

CO

3

2

 

OH

  

At the final titration endpoint, all forms of carbonate have been converted to the carbonic acid (H

2

CO

3

) form. The final pH of the solution, the solution remaining being H

2

CO

3

and H

2

O, is 4.5.

Two indicators 1 , methyl orange and phenolphthalein are added to a sample at specific pH points to assist in identifying the critical endpoints where: 1 st

endpoint - the dominate carbonate species are converted to bicarbonate, and 2 nd

endpoint - where the dominate bicarbonate species are converted to carbonic acid.

1 A compound having a physical property (usually color) that changes abruptly near the equivalence point of a chemical reaction.

When the pH of a sample is above 8.3 carbonate (CO

3

-2

) and bicarbonate (HCO

3

-

) coexist, therefore a phenolphthalein indicator is used. Titration is done to endpoint of pH 8.3, where bicarbonate (HCO

3

) becomes the only carbonate form, just below pH 8.3 bicarbonate and carbonic acid coexist. We will titrate to this endpoint first if the initial sample pH is

8.3

. A methyl orange indicator is used next to indicate the final endpoint point of a pH 4.5. The final specie remaining will be carbonic acid at pH of 4.5 or lower.

The H + added is the amount of acid (usually from a burette and at a 0.02M concentration) required for the following reactions:

H

 

HCO

3

 

H

2

CO

3

2 H

H

CO

3

2

OH

H

H

2

O

2

CO

3

(Consumes H

+

)

Procedure for Laboratory Alkalinity Titration Test

1.

Using the graduated cylinder provided measure 50 mL’s of each of the four samples plus the standard (each group 5 samples in total) into a designated 125 mL Erlenmeyer flask.

2.

Measure and record the initial pH and conductivity of each sample.

3.

If the pH is

8.3 add 4-5 drops of phenolphthalein to each respective sample. If the pH is less than 8.3 go to Step 5

4.

Begin titration, measure and record pH after the addition of each 1 mL of titrant. As you approach a pH of 5.75 reduce the addition of titrant to 0.25 mL. Below a pH of 5.25 only add a few drops at a time and finally below pH of 5.0, drop by drop. GO SLOW: practice without the sample under the burette. GO DROP BY DROP.

***Record the volume of the titrant at the point it becomes colorless and record the pH.

***** If the solution turns colorless before titrating, record the pH again, and proceed to Step

5 .*****

5.

Add 5 drops of Methyl Orange indicator using a dropper, and titrate again. When you first add the Methyl Orange the color should be a yellow color . Measure and record pH after the addition of each 1 mL of titrant. GO SLOW: practice without the sample under the burette.

GO DROP BY DROP. Record the volume of titrant when the solution becomes a light goldorange color , and then record its final pH. If the pH is not at 4.5 then you may want to add another drop or two of titrant.

2

Questions

1) Could anything other then OH

-

, HCO

3

-

and CO

3

2-

contribute to alkalinity? If so what and how?

2) Why does the phenolphthalein turn clear immediately when added to all the Bushkill samples? Explain in a clear and precise manner.

3) Explain whether or not your results make sense, based on what you know about the watershed geology. Which part of the stream is better equipped (i.e., buffered) to neutral acid from acid rain?

4) For the acid titrations your group performed in the laboratory plot pH vs.Volume of acid.

Provide comment.

5) The 0.02 N solution of sulfuric acid was prepared ahead of time by diluting 2.8 mL of concentrated H

2

SO

4

(

= 1.835 g/cm3) into 1000 mLs of deionized water, and diluting this solution by a factor of 5. Show that this procedure results in a 0.02 N solution of H

2

SO

4

.

What to Hand In

1) One set of questions and results for each group.

2) Data and calculations neatly presented.

When is it due?

Next lab period

3

Calculation from Alkalinity Measurements Alone:

In this procedure, phenolphthalein and total alkalinity's are determined, and from these measurements the calculation of three types of alkalinity, hydroxide, carbonate, and bicarbonate, are made. This can be done by assuming (incorrectly) hydroxide and bicarbonate alkalinity cannot exist together in the sample. This permits only five possible situation to be present, which are as follows: 1) hydroxide only, 2) carbonate only, 3) hydroxide plus carbonate, 4) carbonate and bicarbonate, and 5) bicarbonate only.

Hydroxide only - Samples containing only hydroxide alkalinity have a high pH, usually well above 10. Titration is essentially complete at the phenolphthalein end point. In this case hydroxide alkalinity is equal to the phenolphthalein alkalinity.

Carbonate only - Samples containing only carbonate alkalinity have a pH of 8.3 or higher. The titration to the phenolphthalein end point is exactly equal to onehalf of the total titration. In this case carbonate alkalinity is equal to the total alkalinity.

Hydroxide-Carbonate - Samples containing hydroxide and Carbonate alkalinity have a high pH, usually well above 10. The titration from the phenolphthalein to the methyl orange end point represents one-half of the carbonate alkalinity.

Therefore carbonate alkalinity make be calculated as follows:

Carb. alk.= 2 (titration from phenol. to methyl orange) x ml

1000 sample and

Hydroxide alk. = total alk. - carbonate alk.

Carbonate-bicarbonate - Samples containing carbonate and bicarbaonate alkalinity have a pH > 8.3 and usually less than 11. The titration to the phenolphthalein end point represents one-half of the carbonate. Carbonate alkalinity may be calculated as follows:

Carb. alk. = 2 (titration to phenol. end point) x ml

1000 sample and

Bicarbonate alk. = total alk. - carbonate alk.

4

Bicarbonate only - Samples containing only bicarbonate alkalinity have a pH of

8.3 or less, usually less. In this case bicarbonate alkalinity is equal to the total alkalinity.

*This is an approximate method to determine the type of alkalinity present.

Figure 1 - Graphical representation of titration of samples containing various forms of alkalinity.

5

Data Sheets

Calculations

Phenolphthalein alkalinity (as mg/L of CaCO

3

) =

A x N mL of x 50 , 000 sample

Total alkalinity (as mg/L of CaCO

3

) =

B x N mL of x 50 , 000 sample

Where: A = mL of acid to reach Phenolphthalein end point

B = mL of acid to reach Methyl Orange end point

N = Normality of acid

Reagents

Titrant: 0.02 N H

2

SO

4

Standard Solution: 3 x 10

-3

M NaHCO

3

Indicators: Phenolphthalein (P) and Methyl Orange (M)

Apparatus for Laboratory Alkalinity Test pH/conductivity Meter, 6 Erlenmeyer flasks (one extra for practice), 1 Burette, Pipettes, P & M

Indicators w/droppers, 1 small beaker to hold DI rinse water, 1 small beaker to collect samples

(about 75 ml – once collected, measure 50 ml using graduated cylinder), 1 large beaker for w/w

Final Data

Alkalinity Sample

Standard

Tap Water

Sobers Run

L. Bushkill

U. Shoeneck

Shoeneck

B. Shoeneck

13 Street

Conductivity pH

6

Standard

Volume

Tap Water Sobers Run Little Bushkill pH Volume pH Volume pH Volume pH

7

Above Shoeneck

Volume

Shoeneck

Below

Shoeneck

13 th Street pH Volume pH Volume pH Volume pH

8

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