Chemical characteristics of sewage/Waste water/total solid, suspended solid and Dissolved solid and Settleble solid/pH values/BOD and COD/Biochemical Oxygen Demand/Per capita Load/Chemical Oxygen Demand/Nitrogen/Dissolved Oxygen/DO/Sanitary Engineering/Environmental Engineering
Chemical characteristics of Sewage
Chemical
characteristics of sewage indicate the sewage pollution extent and the type of
treatment required. The basic chemical characteristics with test for
determining are:
a. Total solid, Suspended and Dissolved solid and Settleble Solid:
Present in small amount (0.1%), solid can be in four different forms. These solids can be both organic and inorganic matter. Organic matter consist of carbohydrate, fat, nitrogenous compounds etc. and inorganic matter consist of minerals and salts.
Total solid is the sum of all kind of solid.
The estimation of suspended solids, both organic and inorganic, gives a general picture of the load on sedimentation and grit removal system during sewage treatment. Dissolved inorganic fraction is to be considered when sewage is used for land irrigation or any other reuse is planned.
Suspended solid:
solids whose specific gravity are lighter and remains in floating stage.
Dissolved solid: those solids that are in dissolved stage in waste water.
Settleble solids: Those portions of solids (organic or inorganic) matter which settles out if sewage is allowed to remain undisturbed for a period of 2 hours.
b. pH Values:
pH of sewage represents the –ve logarithm of concentration of hydrogen ion. It is a valuable parameter in the operation of biological units. The pH of the fresh sewage is slightly more than the water supplied to the community. However, decomposition of organic matter may lower the pH, while the presence of industrial wastewater may produce extreme fluctuations. Generally the pH of raw sewage is in the range 5.5 to 8.0.
ORGANIC MATTER
Heterogenous mixture of various organic compounds, Main component carbohydrate, protein and fats. Organic matter are determined by two method.
Direct method: This involves determination of total organic carbon.
Indirect method: BOD5, COD and ultimate BOD
BOD and COD
Organic compounds present in sewage are of particular interest for environmental engineering. A large variety of microorganisms (that may be present in the sewage or in the receiving water body) interact with the organic material by using it as an energy or material source. The utilization of the organic material by microorganisms is called metabolism. To describe the metabolism of microorganisms and oxidation of organic material, it is necessary to characterize quantitatively concentration of organic matter in different forms. In view of the enormous variety of organic compounds in sewage it is totally unpractical to determine these individually. Thus a parameter must be used that characterizes a property that all these have in common. In practice two properties of almost all organic compounds can be used:
(1) organic compound can be oxidized; and
(2) organic compounds contain organic carbon.
In environmental engineering there are two standard tests based on the oxidation of organic material:
1) The Biochemical Oxygen Demand (BOD) and Chemical Oxygen Demand (COD) tests.
In both tests, the organic material concentration is measured during the test. The essential differences between the COD and the BOD tests are in the oxidant utilized and the operational conditions imposed during the test such as biochemical oxidation and chemical oxidation. The other method for measuring organic material is the development of the Total Organic Carbon (TOC) test as an alternative to quantify the concentration of the organic material.
Biochemical Oxygen Demand (BOD):
The BOD of the sewage is the amount of oxygen required for the biochemical decomposition of biodegradable organic matter under aerobic conditions. The oxygen consumed in the process is related to the amount of decomposable organic matter. The general range of BOD observed for raw sewage is 100 to 400 mg/L
PER CAPITA LOAD
Chemical Oxygen Demand(COD)
The COD gives the measure of the oxygen required for chemical oxidation. It does not differentiate between biological oxidisable and nonoxidisable material. However, the ratio of the COD to BOD does not change significantly for particular waste and hence this test could be used conveniently for interpreting performance efficiencies of the treatment units. In general, the COD of raw sewage at various places is reported to be in the range 200 to 700 mg/L. In COD test, the oxidation of organic matter is essentially complete within two hours, whereas, biochemical oxidation of organic matter takes several weeks. In case of wastewaters with a large range of organic compounds, an extra difficulty in using BOD as a quantitative parameter is that the rate of oxidation of organic compounds depends on the nature and size of its molecules. Smaller molecules are readily available for use by bacteria, but large molecules and colloidal and suspended matters can only be metabolized after preparatory steps of hydrolysis. It is therefore not possible to establish a general relationship between the experimental five-day BOD and the ultimate BOD of a sample, i.e., the oxygen consumption after several weeks. For sewage (with k=0.23 d-1 at 20oC) the BOD5 is 0.68 times of ultimate BOD, and ultimate BOD is 87% of the COD. Hence, the COD /BOD ratio for the sewage is around 1.7.
C. Nitrogen
The presence of nitrogen in sewage indicates the presence of organic matter, the principal nitrogen compounds in domestic sewage are proteins, amines, amino acids, and urea. The various form of nitrogen in sewage are
i. Free ammonia
ii. Albuminoidal nitrogen called organic nitrogen
iii. Nitrites
iv. Nitrates
Ammonia nitrogen in sewage results from the bacterial decomposition of these organic constituents and indicates the very first state of decomposition. Nitrogen being an essential component of biological protoplasm, its concentration is important for proper functioning of biological treatment systems and disposal on land. Generally, the domestic sewage contains sufficient nitrogen, to take care of the needs of the biological treatment. For industrial wastewater if sufficient nitrogen is not present it is required to be added externally.
Albuminoid nitrogen indicates the quantity of nitrogen present in sewage before the decomposition of the organic matter is started.
Nitrites indicate the presence of partly decomposed organic matter.
Nitrate indicates the presence of fully oxidized organic matter.
The test on nitrogen confirms the decomposition stage of organic matter. For example if nitrite is present then it indicates incomplete decomposition however if nitrate is present it shows that sewage is well oxidized. It is however important to limit the concentration of nitrate before disposal as it may cause nitrate poisoning.
In infant it nitrate
rich water causes blue baby disease. Nitrogen compound leads to a phenomenon of
eutrophication.
In the process of conversion of ammonia to nitrite and nitrate, oxygen are consumed this reduces DO content.
Free ammonia is measured by boiling of sewage and measuring the gas.
Albuminoid nitrogen is measure by adding potassium permanganate to the boiled sewage. If unboilded sample is used to add potassium permanganate, it gives the sum of ammonia nitrogen and organic nitrogen which is known as kjedahl nitrogen.
Nitrite is measured by color matching method by adding sulphonilic acid and napthamine. Nitrates is measured by adding phenol di sulphonic acid and potassium hudroxide. Generally nitrogen content in the untreated sewage is observed to be in the range of 20 to 50 mg/L measured as TKN or 45 ppm nitrate.
d. Phosphorus:
Phosphorus is contributing to domestic sewage from food residues containing phosphorus and their breakdown products. The use of increased quantities of synthetic detergents adds substantially to the phosphorus content of sewage. Phosphorus is also an essential nutrient for the biological processes. The concentration of phosphorus in domestic sewage is generally adequate to support aerobic biological wastewater treatment. However, it will be matter of concerned when the treated effluent is to be reused. It is essential for microorganism growth but in excess amount it leads to eutrophication.The concentration of PO4 in raw sewage is generally observed in the range of 5 to 10 mg/L.
e. Cloridshe:
Municipal water contains large quantity of chlorides, derived form the kitchen wastes, human feaces and urinary discharges etc. The normal chloride content is 120 ppm however in water supplies it is accepted to 250ppm.
Concentration of chlorides in sewage is greater than the normal chloride content of water supply. The chloride concentration in excess than the water supplied can be used as an index of the strength of the sewage. The daily contribution of chloride averages to about 8 gm per person. Based on an average sewage flow of 150 LPCD, this would result in the chloride content of sewage being 50 mg/L higher than that of the water supplied. Any abnormal increase should indicate discharge of chloride bearing wastes or saline groundwater infiltration, the latter adding to the sulphates as well, which may lead to excessive generation of hydrogen sulphide.
Dissolved oxygen DO
DO content represents the amount of oxygen in dissolved state in sewage. It is an important parameter that indicates the purity of water and hence waste water. In case of sewage, if it is too polluted, a situation may arise when it has no DO content, in such cases it becomes important to increase the DO content of sewage by aeration. Presence of DO content facilitates aerobic decomposition of waste water. After treatment, it is important that sewage contain at least 4 ppm DO content before disposing to the receiving water value. 4 ppm DO content is required to maintain the aquatic life of the water bodies. It is determined by wrinklers method in lab.
Oil and grease: These are fraction of organic matter that are soluble in hexane. It constitutes about 10 % of total organic matter.
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