CEE 772

Fall 2005

 

Homework #2

 

 

Use the following TOX raw data to answer the following questions:

 

 

 

Integrated Peak (ng)

Sample

Volume (mL)

1st column

2nd column

distilled water

50

605

555

200 ug/L MCAA

50

2405

1205

100 ug/L MCAA

50

1490

890

Tap Water

50

3492

1955

Tap Water

50

4059

1538

distilled water

50

510

660

groundwater

100

1288

799

groundwater

100

1892

865

groundwater

100

1484

990

groundwater

100

1553

921

groundwater

100

1399

1020

groundwater

100

1686

952

groundwater

100

1335

1100

distilled water

50

495

600

 

 

  1. What is the TOX concentration of the tap water sample?
  2. Are the two GAC cartridges adequately capturing the organic halogen compounds?
  3. What is the % recovery of the MCAA standards?
  4. What is the method detection limit? (refer to section 1030 in Standard Methods for this)

 

 

Solution

 

  1. What is the TOX concentration of the tap water sample?

 

For this you must first calculate an average blank value from the distilled water replicates.

 

Blank Avg =

570.8

 

Then you subtract this blank from the individual column values to get the net organic halide in ng (as Cl).  Finally you add the two net values and divide by the sample volume to get the TOX concentration in ug/L.  See table below for these calculations:

 

 

 

Integrated Peak (ng)

 

Net OX (ng)

 

TOX

MCAA

% recovery

Sample

Volume (mL)

1st column

2nd column

Sum

1st

2nd

sum

% first

conc (ug/L)

conc (ug/L)

 

distilled water

50

605

555

1160

34

-16

18

 

 

 

 

200 ug/L MCAA

50

2405

1205

3610

1834

634

2468

74%

49.4

200

65.8%

100 ug/L MCAA

50

1490

890

2380

919

319

1238

74%

24.8

100

66.0%

Tap Water

50

3492

1955

5447

2921

1384

4305

68%

86.1

 

 

Tap Water

50

4059

1538

5597

3488

967

4455

78%

89.1

 

 

distilled water

50

510

660

1170

-61

89

28

 

 

 

 

groundwater

100

1288

799

2087

717

228

945

76%

9.5

 

 

groundwater

100

1892

865

2757

1321

294

1615

82%

16.2

 

 

groundwater

100

1484

990

2474

913

419

1332

69%

13.3

 

 

groundwater

100

1553

921

2474

982

350

1332

74%

13.3

 

 

groundwater

100

1399

1020

2419

828

449

1277

65%

12.8

 

 

groundwater

100

1686

952

2638

1115

381

1496

75%

15.0

 

 

groundwater

100

1335

1100

2435

764

529

1293

59%

12.9

 

 

distilled water

50

495

600

1095

-76

29

-47

 

 

 

 

 

 

 

 

Tap Water Mean =

 

 

87.6

 

 

 

 

 

 

Groundwater Standard Deviation =

2.1

ug/L

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

MDL  = 3.14*SD =

6.6

ug/L

 

 

 

The values for the two tap water samples are 86.1 and 89.1 ug/L.  So the average would be 87.6 ug/L

 

 

  1. Are the two GAC cartridges adequately capturing the organic halogen compounds?

 

Here you compare the net values from the first column with those from the second column.  This may be done as a %age of the first compared to the total.  Results of this calculation are shown in the table above under the column “% first”.  These values average about 85%, and the lowest is for the first tap water sample at 70%.  This is good recovery as only 30% of 30% (or 9%) would be escaping the second column, even in this worst sample.

 

 

 

 

 

 

  1. What is the % recovery of the MCAA standards?

 

Here you need to recognize that MCAA is only 37.5% chlorine by weight.  Therefore you expect to get 37.5 ug/L and 75 ug/L for the two standards.  The actual values fall well below, and they average 65.9 % of the expected value (see table above).

 

 

 

 

  1. What is the method detection limit? (refer to section 1030 in Standard Methods for this)

 

Based on standard methods you need 7 replicates of a low level sample.  The groundwater sample serves our purpose here.  First you calculate the standard deviation of those 7 samples.  This turns out to be 2.1 ug/L.  Then you multiply by the appropriate t-statistic (i.e.,  3.14) which gives us an MDL of 6.6 ug/L (see above).

 

 

 

 

Assigned: 24 Oct 2005

Due: 31 Oct 2005