Lecture 4- Water Conditioning

Post on 11-Aug-2015

26 views 4 download

Tags:

Transcript of Lecture 4- Water Conditioning

04/13/23 Ballice, 2009 1

INORGANIC TECHNOLOGY

Prof. Dr. Levent Ballice

04/13/23 Ballice, 2009 2

In order to treat water, we must understand it and be able to describe it as much detail as possible.

Certain expressions used in water treatment are far removed from usual scientific terminology.

04/13/23 Ballice, 2009 3

The most comman of these are listed below.

Turbidity

Together with the measurement of suspended solids, this gives an initial indication of the level of colioidal matter of inorganic or organic origin. Turbidity is judged either by comparing the specimen with reference opalescent solutions (formazin, etc.) or by measuring the limit of visibility using a well-defined object (a platinum wire or a Secehi disc).

04/13/23 Ballice, 2009 4

The Fouling indexThe Fouling index

It is a measure of the fouling potential of water. It is also linked with suspended solids and is involved in water treatment by membranes.

04/13/23 Ballice, 2009 5

Suspended solids (SS)

This includes all matter suspended in water that is large enough to be retained on a filter with a given porosity

04/13/23 Ballice, 2009 6

Colour

True colour after filtration is due most often to the presence of dissolved or colioidal organic marter.

There is no relationship between the colour and the quantity of organic matter.

Colour is measured by comparing the specimen with a reference solution (Platinum-Cobalt method).

04/13/23 Ballice, 2009 7

Concentration (by volume)

This is a measure of the quatity of matter dissolved or dispersed in a given volume of water.

As an example, it is mg/L, g/m3, g/L

04/13/23 Ballice, 2009 8

Gramme-equivalent

The gramme-equivalent is equal to the molar weight of a substance divided by the number of charges of the same sign carried by the ions released by a molecule of that substance in an aqueous solution.

04/13/23 Ballice, 2009 9

For instance,

a molecule of orthophosphoric acid, H3P04, releases three positive charges and three negative charges. One gramme-equivalent of H3PO4 is therefore equal to one third of the weight of one mole of H3PO4 .

04/13/23 Ballice, 2009 10

Normality

A normal solution is one comaining one gramme-equivalent of the relevant substance per litre. Multiples and submultiples of the normal solution are also used (2N, N/10, N/25, N/50, N/100, etc. solutions).

04/13/23 Ballice, 2009 11

In general, when a volume V1 of an electrolyte of normality N2 is acted upon another electrolyte of normality N2, the volumeV2 is determined from the relation:

N1V1= N2V2

04/13/23 Ballice, 2009 12

Milliequivalent per liter

The unit often used in practice is the milliequivalent per liter (meq./L) which is obtained by dissolving a quantity of the electrolyte equal to one thousandth of its gramme-equivalent in one liter of water. This is the concentration of an N/1000 solution.

04/13/23 Ballice, 2009 13

The French degree

The unit used in practical water treatment is the French degree which corresponds to the concentration of an N/5000 solution.

1 meq/L = 5 French degrees

04/13/23 Ballice, 2009 14

Examples:

A solution of a calcium salt at 25 French degrees contains in Calcium (of molar weight 40 g an valency 2):

(40 x 5) / 2x 1000 = 0.1 g per liter

04/13/23 Ballice, 2009 15

The equivalance of various degrees

1 French degree = 0.56 German degree = 0.7 English degree = 10 ppm CaCO3

1 German degree = 1.786 French degree = 0.25 English degree = 17.86 ppm CaCO3

1 ppm CaCO3 = 0.1 French degree = 0.056 German degree = 0.07 English degree

04/13/23 Ballice, 2009 16

Titration for hardness (TH):

The titration for hardness indicates the concentration of alkaline-earth ions in water.

04/13/23 Ballice, 2009 17

The various types:

(A) Total TH: content of Ca and Mg.

(B) Calcium TH: content of Ca.

(C)Carbonate hardness: content of bicarbonates and carbonates of Ca and Mg.

04/13/23 Ballice, 2009 18

(D) Noncarbonate hardness (permanent hardness):

Indicates the content of Ca and Mg corresponding to strong anions. It is equal to the difference between A and C.

04/13/23 Ballice, 2009 19

Phenolphthalein alkalinity (P alk.) and methyl orange alkalinity (M alk.)

The relative values of P alk. and M alk. indicate the quantities of alkaline or alkaline earth hydroxides, carbonates or bicarbonates in water.

The P alk. value therefore includes all the hydroxide content but only half of the carbonate content.

04/13/23 Ballice, 2009 20

The M alk. therefore incidate the bicarbonate content.

In some very polluted waters, the M alk also covers organic acids.

04/13/23 Ballice, 2009 21

Measurements of salts of strong acids (SSA):

Natural waters contains no free strong acids but only their salts, in particular the sulphates and chlorides of calcium, magnesium and sodium. The SSA expresses the total content of these salts of strong acids.

04/13/23 Ballice, 2009 22

Salinity

The overall salinity of water corresponds to the total number of cations and anions as expressed in mg/L.

04/13/23 Ballice, 2009 23

Permanganate value:

All substances susceptible to oxidation by potassium permanganate (KMnO4).

04/13/23 Ballice, 2009 24

Chemical oxygen demand (COD)

The COD indicates the total hot oxidation by potassium dichromate and covers the majority of organic compounds as well as oxidizable mineral salts.

04/13/23 Ballice, 2009 25

Biochemical oxygen demand (BOD)

This is the quantity of oxygen consumed at 20 oC and in darkness during a given period to produce by biological means oxidation of the biodegradable organic matter present in water.

04/13/23 Ballice, 2009 26

By convention, BOD5 is used, which is the quantity of quantity of oxygen consumed after five days’ incubation. BOD5 normally represents only the biodegradable carbonaceous organic pollution.

04/13/23 Ballice, 2009 27

Total organic carbon (TOC)

This indicate the content of carbon linked to organic material by measuring the CO2 after complete oxidation.

04/13/23 Ballice, 2009 28

04/13/23 Ballice, 2009 29

04/13/23 Ballice, 2009 30

04/13/23 Ballice, 2009 31

04/13/23 Ballice, 2009 32

04/13/23 Ballice, 2009 33