Monday, 2 July 2012

How to determine Chemical Oxygen Demand (COD) of Waste water

Definition:


Chemical oxygen demand (COD) - The mass concentration of oxygen equivalent to the amount of dichromate consumed by dissolved and suspended matter when a water sample is treated with that oxidant under defined conditions.

Preparing Reagents:


Water:

All blank and reagent water must have a conductivity of less than 2 microsiemens per centimeter, a Total Organic Content of less than 1 mg/l C and be free from reducing agents.
Distilled or deionised water can be used provided the blank remains acceptable.

Sulphuric acid (d20 1.84):

            Unacceptable blank values can be caused by minute amounts of contaminants in the reagents. The major cause is the sulphuric acid used, analytical reagent grade is necessarily better than ordinary acid, and when satisfactory batch has been found it should be reserved for COD use only.

1% m/v Silver sulphate in sulphuric acid:

Dissolve 5.0±0.05g of silver sulphate in 500 ml of sulphuric acid (d20 1.84). To obtain a satisfactory solution the initial mixture should be shaken allowed to stand overnight and then shaken again in order to dissolve all the silver sulphate. Store in a dark brown glass bottle out of direct sunlight.
 
Mercuric sulphate solution:

Dissolve 100±1g mercuric sulphate in a mixture of 500 ml water and 50±2ml sulphuric acid (d20 1.84). The microanalytical reagent grade of mercuric sulphate is advised when measuring very low COD values.

 
Standard reference solution of potassium dichromate 0.02083M (M/48)

Dissolve 6.129±0.001g of Analar potassium dichromate, previously dried at 140 - 150 oC in water and make up to one liter in calibrated flasks.

1:10 phenanthroline ferrous complex (Ferroin)

This reagent is commercially available in either plastic or glass bottles: both are acceptable. If necessary a suitable indicator can be prepared as follows. Dissolve 3.5±0.1g ferrous sulphate heptahydrate in 500±1ml of water. Add 7.4±0.1g of 1:10 phenanthroline monohydrate and shake until dissolved.

Standard solution of ferrous ammonium sulphate 0.0125M

Add 40 ml of sulphuric acid (d20 1.84) to 400 ml water, mix and cool. Dissolve 9.803 g of ferrous ammonium sulphate hexahydrate in the cooled dilute acid and make up to 2 litres in a calibrated flask.

Preparation from solid

Standardise the solution, each day before use, against the standard potassium dichromate as follows:

Prepare a stock of diluted sulphuric acid by adding 375±5ml of sulphuric acid (d20 1.84) to 600 ±5ml of water and cool. To a 50 ml flask add 19.5 ml of diluted sulphuric acid, followed by 2.0 ml of 0.02604M potassium dichromate solution and titrate with ferrous ammonium sulphate using not more than two drops of Ferroin as indicator. The color change is from blue-green to pink. Alternatively the diluted sulphuric can be made up in
Situ by adding 7.5-ml sulphuric acid (d20 1.84) to 12 ml of water in a 50 ml flask and cooled. It is important to add the dichromate after the diluted sulphuric acid has cooled to avoid the oxidation of any organic contaminants by the dichromate before it can be titrated.

Standard reference solution of potassium hydrogen phthalate, COD of 200 mg/l

            Dissolve 0.1701±0.001g of potassium hydrogen phthalate, previously dried at 120 oC for 2 hours, in water and dilute to one liter in a calibrated flask. The standard must be stored, without freezing, in a refrigerator and be renewed monthly.

Standard reference solution of potassium hydrogen phthalate, COD of 400 mg/l

            Use 0.340±0.001g of potassium hydrogen phthalate.

Standard reference solution of potassium hydrogen phthalate, COD of 800 mg/l

            Use 0.680±0.001g of potassium hydrogen phthalate.


PROCEDURE:


All operations must be carried out with care. If any difficulties arise during the course of the analysis, then these must reported immediately to the operator's supervisor.

Digestion:
1. The boiling point of the reaction mixture is defined by the ratio of sulphuric acid to  
     water present; therefore the reagent and sample volumes used must be kept 
     constant.

2. Insert the anti-bumping aid or granules into the boiling flask.
    Measure 5 ml±0.03 ml of sample into the flask.

 3. Add 0.5 ml of mercuric sulphate solution and swirl to mix. Add 2.0±0.01 ml 0.0283M 
    potassium dichromate and 7.5±0.1ml m/v silver sulphate in concentrated sulphuric 
    acid.

4. Fit the condenser and swirl the flask and its contents, and boil gently under reflux for 2 
    hours ± 10 min.

 5. Remove the flask from the source of heat and allow to cool for approximately 10 min 
     then add 10±5 ml of water via condenser. Disconnect the flask from the condenser 
     and cool the flask to room temperature in running water. Determine the residual 
     dichromate by titration.


 Determination of residual dichromate:

1. Add not more than two drops of Ferroin indicator to the flask and titrate the residual dichromate with             standardized ferrous ammonium sulphate. Empty residual solutions into special container for disposal     by chemical stores, then rinse flask with tap water and then de-ionized water.

            2. Blank Determination
Ideally the blank value should be the mean of at least three determinations, but if any value differs by more than ±0.5 ml from the mean value it must be rejected and a new mean recalculated from the acceptable blank values, additional determinations being made if necessary.


STANDARD DETERMINATION:

With each of the samples run potassium hydrogen phthalate standards. Take a 5.0 ml aliquot of the standard potassium hydrogen phthalate solutions and carry out the determinations.

1.  Once in the position they need not be removed between determinations.

2.    If necessary, the sample should be diluted accurately and a 5 ml aliquot taken for 
    oxidation, which should consume dichromate equivalent to between 5.0 and 20 ml of 
    0.0125M ferrous ammonium sulphate.

3 . Use a grade A pipette or micro burette to add the potassium dichromate.


4 Run the acid down the side of the flask whilst gently swirling. Carry out this operation 
    in a fume cupboard. When samples are known to contain volatiles, cool the flask 
    under running cold water to minimize loss of volatiles.

5.  The amount of mercuric sulphate in this mixture will suppress, but not entirely 
    eliminate, the effect of chloride ion.
 
6. Excessive reflux times may result in high blank values.


7.  After the first addition of ferrous ammonium sulphate solution the indicator is 
    blue-green in color and the endpoint occurs when the color changes sharply to
    through deep blue to pink. The blue colour may reappear a few minutes later but his 
    phenomenon should be ignored.

8. An acceptable blank test should require at least 23.5 ml of 0.0125M ferrous 
    ammonium sulphate or its equivalent, in the titration.

9. This result should be plotted on a control chart. If the standard determination is 
outside the ±3 times the standard deviation limits, some action should be taken to bring 
the method back in control.


CALCULATION OF RESULTS:


            The COD of the samples can be calculated from the following expression:

                       
                        COD mg/l = (T1 - T2) x F x D

                        T1 = average number of ml ferrous ammonium sulphate used to titrate  
                                appropriate blank

                        T2 = number of ml ferrous ammonium sulphate used to titrate sample

                        F = standardization factor for ferrous ammonium sulphate

                                                25
                           = ----------------------------------------------------- x 20*
                              standardization titration, vol. In ml FAS        

                        D = dilution factor

                                total volume of the diluted sample
                            = -----------------------------------------------
                                sample volume taken for dilution

*1.0 ml 0.0125M ferrous ammonium Sulphate is equivalent to 0.10 mg oxygen and is equivalent to 20 mg/l COD with 5.0 ml sample






How to determine Total Suspended Solids in a Sample

Definition:

 
Total Suspended Solids (TSS) or Mixed Liquor Suspended Solids (MLSS) is the part of the Total Solids present in the sample under investigation, which is removed by filtration. The result is given in mg/L.

APPARATUS:


            Vacuum pump
            Suction flask, 250 or 500 ml
            Hartley funnel
            Measuring cylinder, 250ml
            Watch glass, 15 cm dia
            Glass filter fibre paper, 125 mm dia Whatman Cat. No. 1822 125
            Oven, Set at 110 oC
            Dessicator
            Furnace, Set at 500 oC
            Furnace tongs
 

PROCEDURE:


1.             Number the glass fibre filter, bring it on a watch glass and put it into the furnace at 500 oC for 30 min to ensure that any organic material in the paper is removed. The paper should be kept flat and not folded, as it may become brittle if creased.

2.             Remove the filter paper and watch from the furnace, cool in a Dessicator for 15 minutes and weigh (M1).

3.             Place the filter paper in the Hartley funnel. Take care not to crease.

4.             Place the Hartley funnel on the top of the suction flask.

5.             Connect the flask to the vacuum pump, and apply vacuum.

6.             Measure 100 ml mixed effluent sample into a measuring cylinder and pour it through the glass fibre paper.

7.             When all the liquid has passed through the filter paper rinse the measuring cylinder with 10 ml distilled water and pour this through the glass fibre paper.

8.             Repeat the rinsing twice more and then place the paper on the watch glass and dry it in an oven at 110 oC for 1 hour.

9.             Remove the filter paper and watch glass from the oven, cool in a dessicator for 15 min and record the final mass (M2).

10.          Place further filter paper and watch glass in a furnace at 500 oC for 30 min. (The ignition time should be taken from when the furnace actually reaches the required temperature at 500 oC).

11.          Remove the filter paper and watch glass from the furnace and allow to cool in a dessicator for 15 min.

12.          Reweigh the filter paper and watch glass and record the final mass (M3). (The weight loss will due to organic material burning off (VSS) and the solid left behind on the paper will be the inorganic material (FSS).



CALCULATION:

                                                                      (M2 - M1) x 106
Total Suspended Solids (mg/l)   =          --------------------
                                                                                     V

                                                                      (M3 - M1) x 106
Fixed Suspended Solids (mg/l)  =          --------------------
                                                                                     V

                                                                         (M2 - M3) x 106
Volatile Suspended Solids (mg/l)=         --------------------
                                                                                       V

                                                                   M3 - M1
% Fixed Suspended Solids       =          ---------- x 100
                                                                    M2 - M1

% Volatile Suspended Solids     =          100 - % Fixed Suspended Solids