Water Pollution and Control

 Sources and Characteristics of Chemical Industrial wastewater:

Sources of Waste Water:

Wastewater from the chemical industry can come from many sources, including:

Manufacturing: The production of organic chemicals, plastics, synthetic materials, and other chemicals 

Petrochemicals: The production of petrochemicals, such as polymers for plastics and synthetic fibers 

Inorganic chemicals: The production of inorganic chemicals, such as acids and alkalis 

Agricultural chemicals: The production of agricultural chemicals, such as fertilizers, pesticides, and herbicides 

Industrial wastewater can contain a variety of contaminants, including:

·         Organic and inorganic matter: Toxic and hazardous substances, dyes, and metal ions 

·         Impurities: Dissolved contaminants such as salts and light liquids like oils 

·         Interfering substances: Grease, clay, or sand 

·         Pollutants: Microplastics, residues of pharmaceuticals and detergents, viruses, bacteria, fungi, poisons, and heavy metals.

 Characteristics of Industrial Waste Water:

  Wastewater in the chemical industry has many characteristics, including physical, chemical, and biological characteristics: 

·         Physical characteristics

Include temperature, solids, color, odor, and turbidity: 

Temperature: Higher temperatures speed up reaction rates, which can improve the removal of contaminants. 

Solids: Total suspended solids (TSS) and total dissolved solids (TDS) affect turbidity. 

Color: Fresh sewage is usually brown or yellowish, but over time it can turn black. 

Odor: Wastewater with sewage usually has a strong odor. 

Turbidity: Wastewater has higher turbidity due to suspended solids. 

·         Chemical characteristics

Include pH, alkalinity, nitrogen, phosphorus, and other chemical impurities: 

Chemical oxygen demand (COD): A common method to measure organic content 

Total organic carbon (TOC): A common method to measure organic content 

Chlorides, sulfates, and heavy metals: Chemical impurities in wastewater 

·         Biological characteristics

Include organisms like bacteria, algae, protozoa, and viruses: 

Biochemical oxygen demand (BOD): A common method to measure organic content 

Microbial population: A biological characteristic of wastewater 

 

·         Turbidity

Turbidity is a measure of how clear water is, or how many particles are suspended in it. Turbidity is a measurement of how much light is scattered or blocked by particles in water. When water has high turbidity, it appears cloudy or muddy because the particles absorb and scatter light rays. 

Turbidity can be caused by many things, including:

Natural events: Heavy rains, snowmelt, windstorms, and erosion can wash soil, fertilizers, and other materials into waterways. 

Human activities: Logging, mining, agriculture, dredging, and untreated wastewater can all increase turbidity levels. 

Turbidity is measured using turbidity sensors attached to current meters, or by satellite imagery. 

Standards

The World Health Organization recommends that drinking water have a turbidity of no more than 5 NTU

 

·         pH

The pH of water measures how acidic or basic it is, and is an important indicator of water quality: 

The pH scale ranges from 0 to 14, with 7 being neutral. A pH less than 7 indicates acidity, while a pH greater than 7 indicates a base. 

Pure water: Pure water has a pH of 7, which is neutral. 

Tap water: Tap water typically has a pH between 6.5 and 8.5. 

Other common liquids: The pH of some common liquids includes: 

Wine: 2.3–3.8 

Beer: 4.0–5.0 

Milk: 6.3–6.6 

Seawater: 8.3 

You can measure pH with a strip of litmus paper, which changes color depending on whether the substance is acidic or basic: Red: Acidic Blue: Basic

The Environmental Protection Agency (EPA) says that the safe pH range for drinking water is 6.5–8.5. Water with a pH outside of this range is not recommended for drinking. 

 

·         Total Suspended solids

Total suspended solids (TSS) are solid particles in water that are too large to settle and are suspended in the water. TSS can be organic or inorganic in origin and can range in size from a few microns to being visible to the naked eye. 

TSS is a key parameter in water quality assessment and environmental monitoring. It can impact water quality in the following ways: 

·         Turbidity: TSS can make water cloudy, which reduces the amount of sunlight that reaches plants and algae. This can reduce the amount of oxygen produced and photosynthesis activity, which can lead to low-oxygen conditions and dead zones. 

·         Aquatic life: TSS can harm aquatic life in several ways: 

o    Toxic compounds: Solid particles can contain toxic compounds. 

o    Clogged gills: Soil and silt in the water can clog fish gills. 

o    Bury fish eggs: When TSS settles at the bottom of a body of water, it can bury fish eggs and nursery areas. 

·         Wastewater pollution: TSS is a major cause of wastewater pollution. 

TSS is measured in milligrams per liter (mg/l). The amount of TSS can vary depending on the source of the water and any treatments it has undergone. 

TSS can be calculated using the equation:

TSS (mg/L) = (A – B)/C,

Where, A is the final dried weight of the filter in mg

             B is the initial dried weight of the filter in mg

             C is the volume of water filtered in L. 

 

 

 

·         Total solids:

Total solids (TS) in water is the sum of the total suspended solids (TSS) and total dissolved solids (TDS).

Total solids are the amount of foreign matter in water that remains after evaporation and drying at a specific temperature. The solids in water can be volatile (organic) or non-volatile (inorganic or fixed). 

Suspended solids

These are particles that are not chemically bonded to water molecules and do not pass through a 2-micron filter. Examples include silt, clay, plankton, algae, and fine organic debris. 

Dissolved solids

These are particles that are chemically bonded to water molecules and pass through a 2-micron filter. Examples include calcium, chlorides, nitrate, phosphorus, iron, and sulfur. 

Water clarity

High levels of total solids can make water less clear, which reduces the amount of sunlight that can penetrate the water. 

Aquatic organisms

The balance of dissolved solids in water is important for the health of aquatic organisms. Too many dissolved salts can dehydrate organisms, while too few can limit their growth. 

Drinking water

Drinking water typically has a TDS below 500 parts per million (ppm). 

 

·         Biological Oxygen Demand (BOD)

Biochemical oxygen demand (BOD) is a measure of how much oxygen is needed to break down organic matter in water. It's an important indicator of water quality and is used to assess the degree of organic pollution in water. 

BOD is measured by incubating a water sample in the dark at 20°C for five days. The difference in dissolved oxygen between the beginning and end of the incubation period is used to calculate the BOD. 

A higher BOD means that oxygen is depleted more quickly in the water, which can stress, suffocate, and kill aquatic organisms. 

BOD is used in wastewater treatment plants to measure waste loads, the effectiveness of BOD removal, and the concentration of effluent discharged into water bodies. 

Unpolluted natural waters should have a BOD of 5 mg/L or less. Raw sewage may have BOD levels ranging from 150–300 mg/L. 

 

Calculation of BOD:

 The formula to calculate biochemical oxygen demand (BOD) is:

BOD= (DO1−DO2) * Dilution Factor / Volume of Sample

 

Where, DO1 is the dissolved oxygen (DO) measurement at the beginning of the test

             DO2 is the DO measurement after a 5 day period at 68°F (20°C).

             The BOD value is reported in milligrams per liter (mg/L). 

        BOD is a measure of how much oxygen microorganisms consume in water bodies. It's an important parameter for assessing water quality and is used in wastewater treatment plants to measure waste loads and treatment efficiency

 

Example

A 15 ml water sample is diluted to 300 ml with nutrient solution and incubated in the dark for five days at 20 OC. The initial dissolved oxygen concentration is 9.05 mg/l and the final concentration is 4.25 mg/l. The blank for the dilution water decreased in dissolved   oxygen concentration from 9.05 mg/l to 8.80 mg/l. Estiamte BOD 5

 

The formula to calculate biochemical oxygen demand (BOD) is:

BOD= (DO1−DO2) * Dilution Factor / Volume of Sample

 

DO1 is oxygen dissolved in sample = (9.05-4.25) mg/l

                                                           = 4.80 mg/l

DO2 is oxygen dissolved in Blank= (9.05 -8.80) mg/l

                                                         = 0.25 mg/l

Dilution factor= 300

Volume of sample= 15

BOD = (4.80-0.25) * 300/15

          = 91 mg/l

 

·         Chemical Oxygen Demand (COD):

Chemical Oxygen Demand (COD) is a measure of the amount of oxygen required to oxidize organic and inorganic compounds in water. It's used to assess water quality and the amount of organic pollutants in a water body. 

A water sample is oxidized with a strong oxidizing agent, like potassium dichromate (K2Cr2O7), in the presence of a strong acid. The amount of oxidizing agent consumed is then measured, which reflects the COD of the water sample. 

COD can indicate the presence of all forms of organic matter, both biodegradable and nonbiodegradable. High COD levels can be caused by things like solid waste, soluble organic compounds, and emulsified oils. 

COD is used to monitor water treatment plant efficiency, identify pollution sources, and more. It's also used in wastewater management to reduce COD levels. 

The USPH recommends a maximum COD content of 4.0 mg/L for drinkable water, while the World Health Organization recommends a COD content of 10 mg/L.

 

Chemical oxygen demand (COD) is calculated using a laboratory assay that measures the amount of organic matter in a water sample. The COD can be calculated using the following formulas: 

           COD = (C/FW)·(RMO)·32

This formula estimates the COD from the concentration of oxidizable compounds in the sample. 

 COD (mg/l) = (a-b)(N) x 8,000 / sample size (ml)

This formula uses the amount of Fe(NH4)2(SO4)2 used for the blank and sample, the normality of the titrant, and the sample size. 

      COD, mg/L = (B-A)N x 8000/ sample volume, mL

This formula uses the volumes of FAS used in titrating the blank and sample, and the normality of FAS. 

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