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Step into Turbulator Technologies Global’s world of innovation, offering a dynamic range of industrial mixers designed for diverse applications, from high-speed marvels to specialized solutions for food processing, chemical manufacturing, animal feed, petro-chemical, water and wastewater treatment, and agricultural production.
Our differentiator is customization, where we analyze, design, and manufacture mixers and agitators tailored to your unique processes. Yet, our commitment doesn’t end there. We provide hands-on technical support, including training and troubleshooting, ensuring you harness the full potential of our products.
We don’t just deliver equipment; we deliver a promise of excellence. Our experts ensure precise on-site installation, and our maintenance and repair services keep your machinery in prime condition, operating at peak efficiency.
Retrofits are our sustainable touch, upgrading existing mixers and agitators without the need for a complete overhaul, resulting in up to a remarkable 1200% increase in production. Turbulator Technologies Global is more than a provider; we’re your partner in reshaping industrial mixing. Join us on this journey of innovation and progress.
Chemicals Processing
In today’s competitive environment, product success or failure may well depend on making the correct choice of mixer or agitator or a combination. The right choice plays a key role in ensuring product quality and consistency and it helps minimize the cost of production due to failure with full scale commissioning during startup.
Fundamental to the chemical process industries (CPI)–whether specialty or bulk chemicals, pharmaceuticals, food products, minerals processing, environmental protection or other products or activities–is the need for mixing or agitation. The wide variety and complexity of mixing tasks encountered in industrial applications require careful design and scale up to ensure that effective mixing is achieved efficiently. Designs based on a small range of traditional mixers or agitators are no longer economically acceptable. Modern Rotors or impellers and the use of physical or computer modelling can greatly enhance performance and reduce costs. Turbulator’s recent success where an improvement of 1200% increase in production was achieved at Harcros Chemicals in Tampa, FL, USA. (See case study for more information)
Mixing or Agitation tasks falls into six main categories:
1. Blending of miscible liquids.
2. Blending of mixtures with “difficult” rheology’s (Specific Gravity & Viscosity)
3. Suspension of solids or heavy to mix applications such as slurries.
4. Liquid-liquid dispersions.
5. Heat transfer by friction of the Rotor’s unique axial & radial flow properties.
6. Gas-liquid diffusion or impingement.
Different mixing behaviours and rules govern each basic mixing task. To optimize a design, or to scale-up reliably, these behaviours and rules need to be understood and defined. Complex tasks that involve two or more of the above categories require special attention. The controlling task must be identified to determine the design and scale-up rules to be applied.
Gas-liquid dispersion is a complex subject and shas had many significant advances in recent years. Turbulator Technologies Global specialize in gas to liquid transfer with its unique Air Induction system. Whether it is Steam, Air, Dissolved Oxygen, Ammonia Gas, SO2 or SO4, Turbulator has the answer and customize these units for the specific needs.
In addition to agitator design and power requirements, which are fundamental to mixing systems, many other considerations also play a part in maximizing performance. These considerations include mechanical aspects, seal selection, materials of construction and surface finishes to prevent fouling or aid cleaning.
There was a need for a single design that would address both radial and axial flow all-in-one. The Turbulator was born to accommodate this vital need in industry and emerged from one simple, yet complete design.
The unique mixing pattern or Figure-8 of the Turbulator mixer/agitator provides both axial and radial flow inside the mixing vessel as illustrated below.
Weather it is liquid to liquid, solids to liquid or gas dispersion that must take place.
The above can be observed with the videos (Mixing Principal & Aeration with a Draft tube)
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Pulp & Paper Processing
Pulp and paper mills are highly complex and integrate many different process areas including wood preparation, pulping, chemical recovery, bleaching, and papermaking to convert wood to the final product. Processing options and the type of wood processed are often determined by the final product.
The pulp for papermaking may be produced from virgin fibre by chemical or mechanical means or may be produced by the repulping of paper for recycling. Wood is the main original raw material. Paper for recycling accounts for about 50 % of the fibres used – but in a few cases straw, hemp, grass, cotton and other cellulose-bearing material can be used. Paper production is basically a two-step process in which a fibrous raw material is first converted into pulp, and then the pulp is converted into paper. The harvested wood is first processed so that the fibres are separated from the unusable fraction of the wood, the lignin. Pulp making can be done mechanically or chemically. The pulp is then bleached and further processed, depending on the type and grade of paper that is to be produced. In the paper factory, the pulp is dried and pressed to produce paper sheets. Post-use, an increasing fraction of paper and paper products is recycled. Non recycled paper is either landfilled or incinerated.
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Water and Wastewater Treatment
INTRODUCTION
This provides an introduction to wastewater microbiology. Emphasis is placed on microbial biochemistry because it forms the basis for selecting the appropriate unit process for treating. The wastewater as well as establishing the fundamental relationships for design calculations.
ROLE OF MICROORGANISMS
The stabilization of wastewater is accomplished biologically using a variety of microorganisms. The microorganisms convert colloidal and dissolved carbonaceous organic matter into various gases and into protoplasm. Because protoplasm has a specific gravity slightly greater than that of water, it can be removed from the treated liquid by gravity settling. It is important to note that unless the protoplasm produced from the organic matter is removed from the solution, complete treatment will not be accomplished because the protoplasm, which itself is organic, will be measured as BOD in the effluent. If the protoplasm is not removed, the only treatment that will be achieved is that associated with the bacterial conversion of a portion of the organic matter originally present to various gaseous end products. In addition to stabilization of carbonaceous organic matter, some organisms can remove nutrients that are responsible for eutrophication. A focus of the following discussion is the explanation of the environmental factors that promote the growth and biochemistry of these organisms.
CLASSIFICATION OF MICROORGANISMS
Classification by Energy and Carbon Source
The relationship between the source of carbon and the source of energy for the microorganism is important. Carbon is the basic building block for cell synthesis. A source of energy must be obtained from outside the cell to enable synthesis to proceed. The goal in wastewater treatment is to convert both the carbon and the energy in the wastewater into the cells of microorganisms, which can be removed from the water by settling or filtration. Therefore, the processes are designed and operated to encourage the growth of organisms that use organic material for both their carbon and energy source. If microorganisms use organic material as a supply of carbon, they are called heterotrophic. Autotrophs require only CO 2 to supply their carbon needs. Organisms that rely only on light for energy are called phototrophs. Chemotrophs extract energy from organic or inorganic oxidation/reduction reactions. Organotrophs use organic materials, while lithotrophs oxidize inorganic compounds.
Classification by Oxygen Relationship
Bacteria also are classified by their ability or inability to utilize oxygen in oxidation-reduction reactions. Obligate aerobes are microorganisms that must have oxygen. When wastewater contains oxygen and can support obligate aerobes, it is called aerobic.
*In the lexicon of wastewater treatment, this is called biosolids, or, more colloquially, sludge.
WASTEWATER MICROBIOLOGY
Obligate anaerobes are microorganisms that cannot survive in the presence of oxygen.
Wastewater that is devoid of oxygen is called anaerobic. Facultative anaerobes can use oxygen in oxidation/reduction reactions under certain conditions, they can also grow in the absence of oxygen.
MICROBIAL BIOCHEMISTRY
Energy Capture
Living organisms capture energy released from oxidation-reduction reactions. Enzymes are the organic catalysts produced by microorganisms and used by them to speed the rate of energy yielding and cell-building reactions. The major source of energy is oxidation-reduction reactions that involve transfer of electrons from one atom to another or from one molecule to another.
Electron carriers move the electrons from one compound to another. The initial electron donor is called the primary electron donor. The final electron acceptor is called the terminal electron acceptor. In aerobic systems, the spent electron combines with molecular oxygen to form water. The electron carriers may be divided into two classes: those that are diffusible throughout the cell’s cytoplasm and those that are attached to enzymes in the cytoplasmic membrane. The diffusible carriers include the coenzymes nicotinamide-adenine dinucleotide (NAD ) and nicotinamideadenine dinucleotide phosphate (NADP ). NAD is involved in energy-generating ( catabolic ) reactions. NADP + is involved in biosynthetic ( anabolic ) reactions. Electron carriers attached to the cytoplasmic membrane include NADH dehydrogenases, flavoproteins, cytochromes, and quinonnes.
When nitrate is the terminal electron acceptor, the system is called anoxic. When sulphate or carbon dioxide is the terminal electron acceptor, the system is called anaerobic. This energy analysis indicates that the energy available with nitrate as the electron acceptor is similar to that with oxygen, but sulphate and carbon dioxide yield much less energy per NADH.
The practical implication of these calculations of available energy is that there is a hierarchy of oxidation-reduction reactions. Because aerobic oxidation provides more energy for microorganism growth, it will proceed in preference to anoxic (nitrate) oxidation. Likewise, anoxic oxidation will proceed in preference to anaerobic (sulphate and carbon dioxide) oxidation.
The energy is captured by the organism by transferring the energy from intermediate electron carriers to energy carriers. The primary example of an energy carrier is adenosine triphosphate.
Hydrolysis occurs and may be described as the splitting of a polymer by adding water to a covalent bond. The reaction is catalyzed by a hydrolyase enzyme.
The formation of acetyl-CoA * from fatty acids and glucose. An expanded view of the citric acid cycle (also known as the Krebs cycle after its author, or the tricarboxylic acid cycle ) Two new compounds are introduced.
Fats Carbohydrates Proteins
The three general stages of catabolism of fats, carbohydrates, and proteins under
aerobic conditions. Reversing the processes gives anabolism.
Aerobic Decomposition
Molecular oxygen (O2) must be present as the terminal electron acceptor for decomposition to proceed by aerobic oxidation. The oxygen is measured as dissolved oxygen (DO). When oxygen is present, it is the only terminal electron acceptor used. The chemical end products of decomposition are primarily carbon dioxide, water, and new cell material. Odiferous gaseous end products are kept to a minimum. In healthy natural water systems, aerobic decomposition is the principal means of self-purification. A wider spectrum of organic material can be oxidized aerobically than by any other type of decomposition. This fact, coupled with the fact that the final end products are oxidized to a very low energy level, results in a more stable end product (i.e., one that can be disposed of without damage to the environment and without creating a nuisance condition) than can be achieved by the other oxidation systems. Because of the large amount of energy released in aerobic oxidation, most aerobic organisms are capable of high growth rates. Consequently, there is a relatively large production of new cells in comparison with the other oxidation systems. This means that more biological sludge is generated in aerobic oxidation than in the other oxidation systems. Aerobic decomposition is the method of choice for large quantities of dilute wastewater (BOD 5 less than 500 mg/L) because decomposition is rapid, efficient, and has a low odor potential. Typically, aerobic decomposition is not suitable for high strength wastewater (BOD 5) is greater than 1,000 mg/L) because of the difficulty in supplying enough oxygen and because of the large amount of biological sludge produced. However, in small communities and in special industrial applications where aerated lagoons are used, wastewater with BOD 5 up to 3,000 mg/L may be treated satisfactorily by aerobic decomposition. This is because the daily influent volume of wastewater is small, the detention time is long, and the lagoon acts as a complete mix reactor. Environmental Factors. Steady state rbCOD or acetate availability is required for good phosphorus removal. Periods of starvation or low rbCOD concentrations result in lowering of intracellular storage reserves of glycogen, PHB, and polyphosphates. This leads to decreased phosphorus removal efficiency. This is a potential scenario at start-up of the plant when wastewater flow rates and loads are low. It is also a potential scenario during the diurnal cycle of BOD load because of nighttime decreases in anthropogenic activity.
Systems with excessive anaerobic contact times and without significant VFA production will experience phosphorus release with no uptake of acetate. Excessive anaerobic contact results in the release of orthophosphate without the addition of acetate as the bacteria use stored polyphosphate for an energy source. During subsequent aeration, the oxidation of PHB provides energy for bacteria to assimilate not only the released phosphorus but additional phosphorus from the influent wastewater to build polyphosphate reserves. Not all of the phosphorus that is released in the absence of acetate consumption can be taken up because there is not enough PHB storage to provide the energy for excess uptake during the aerobic period.
Likewise, excessive aeration time will result in less phosphorus uptake. This is the result of the competitive role of glycogen in the formation and utilization of PHB. It may be noted that glycogen is degraded under anaerobic conditions to provide energy for PHB formation. Under aeration a portion of the PHB is converted to glycogen. If less glycogen is available during anaerobic contact, then less PHB formation is expected. Less PHB results in less phosphorus uptake during aeration. If glycogen reserves are depleted in the aerobic period because of excessive aeration, a greater portion of the PHB formed is used to replenish glycogen reserves.
This results in less PHB available for phosphorus uptake under aerobic conditions.
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Petro Chemical
The constant demand for hydrocarbon products such as liquid fuels is one of the major driving forces behind the petroleum industry. However, the other driving force is a major group of hydrocarbon products (petrochemicals) that are the basis of a major industry. There is a myriad of products that have evolved through the short life of the petroleum industry, either as bulk fractions or as single hydrocarbon products. And the complexities of product composition have matched the evolution of the products. In fact, it is the complexity of product composition that has served the industry well and, at the same time, had an adverse effect on product use.
A petrochemical is a chemical product developed from petroleum that has become an essential part of the modern chemical industry. The chemical industry is, in fact, the chemical process industry by which a variety of chemicals are manufactured. The chemical process industry is, in fact, subdivided into other categories that are: (i) the chemicals and allied product industries in which chemicals are manufactured from a variety of feedstocks and may then be put to further use, (ii) the rubber and miscellaneous product industries which focus on the manufacture of rubber and plastic materials, and (iii) petroleum refining and related industries which, on the basis of the following chapters in this text, is now self-explanatory. Thus, the petrochemical industry falls under the subcategory of petroleum and related industries.
In the context of this book, the definition of petrochemicals excludes fuel products, lubricants, asphalt, and petroleum coke but does include chemicals produced from other feedstocks such as coal, oil shale, and biomass, which could well be the sources of chemicals in the future. Thus, petrochemicals are, in the strictest sense, different to petroleum products insofar, as the petrochemicals are the basic building blocks of the chemical industry. Petrochemicals are found in products as diverse as plastics, polymers, synthetic rubber, synthetic fibers, detergents, industrial chemicals, and fertilizers (Table 1.3). Petrochemicals are used for production of several feedstocks and monomers and monomer precursors. The monomers after polymerization process create several polymers, which ultimately are used to produce gels, lubricants, elastomers, plastics, and fibers.
By way of definition and clarification as it applies to the petrochemical and chemical industry, primary raw materials are naturally occurring substances that have not been subjected to chemical changes after being recovered. Currently, through a variety of intermediates petroleum and natural gas are the main sources of the raw materials because they are the least expensive, most readily available, and can be processed most easily into the primary petrochemicals. An aromatic petrochemical is also an organic chemical compound but one that contains, or is derived from, the basic benzene ring system.
Primary petrochemicals include: (i) olefin derivatives such as ethylene, propylene, and butadiene;
(ii) aromatic derivatives such as benzene, toluene, and the isomers of xylene (BTX); and (iii) methanol. However, although petroleum contains different types of hydrocarbon derivatives, not all hydrocarbon derivatives are used in producing petrochemicals. Petrochemical analysis has made it possible to identify some major hydrocarbon derivatives used in producing petrochemicals. From the multitude of hydrocarbon derivatives, those hydrocarbon derivatives serving as major raw materials used by petrochemical industries in the production of petrochemicals are: (i) the raw materials obtained from natural gas processing such as methane, ethane, propane, and butane; (ii) the raw materials obtained from petroleum refineries such as naphtha and gas oil; and (iii) the raw materials such as benzene, toluene and the xylene isomers obtained when extracted from reformate (the product of reforming processes through catalysts called catalytic reformers in petroleum refineries.
Thus, petrochemicals are chemicals derived from petroleum and natural gas and, for convenience of identification, petrochemicals can be divided into two groups: (i) primary petrochemicals and (ii) intermediates and derivatives. Primary petrochemicals include: olefins (ethylene, propylene, and butadiene), aromatics (benzene, toluene, and xylenes), and methanol. Petrochemical intermediates are generally produced by chemical conversion of primary petrochemicals to form more complicated derivative products. Petrochemical derivatives can be made in a variety of ways: (i) directly from primary petrochemicals; (ii) through intermediate products which still contain only carbon and hydrogen; and (iii) through intermediates which incorporate chlorine, nitrogen, or oxygen finished derivative. In some cases, they are finished products; in others, more steps are needed to be arrived at the desired composition.
Moreover, petrochemical feedstocks can be classified into several general groups: olefins, aromatics, and methanol; a fourth group includes inorganic compounds and synthesis gas mixtures of carbon monoxide and hydrogen). In many instances, a specific chemical included among the petrochemicals may also be obtained from other sources, such as coal, coke, or vegetable products.
For example, materials such as benzene and naphthalene can be made from either petroleum or coal, while ethyl alcohol may be of petrochemical or vegetable origin.
Thus, primary petrochemicals are not end products, but are the chemical building blocks for
a wide range of chemical and manufactured materials. For example, petrochemical intermediates are generally produced by chemical conversion of primary petrochemicals to form more complicated derivative products. Petrochemical derivative products can be made in a variety of ways: (i) directly from primary petrochemicals; (ii) through intermediate products which still contain only carbon and hydrogen; and (iii) through intermediates which incorporate chlorine, nitrogen, or oxygen in the finished derivative. In some cases, they are finished products; in others, more steps are needed to arrive at the desired composition. Some typical petrochemical intermediates are: (i) vinyl acetate (CH3CO2CH=CH2) for paint, paper, and textile coatings; (ii) vinyl chloride (CH2=CHCl) for polyvinyl chloride (PVC); (iii) ethylene glycol (HOCH2CH2OH) for polyester textile fibers; and (iv) styrene (C6H5CH=CH2), which is important in rubber and plastic manufacturing. Of all the processes used, one of the most important is polymerization. It is used in the production of plastics, fibers, and synthetic rubber, the main finished petrochemical derivatives.
Following from this, secondary raw materials, or intermediate chemicals, are obtained from a primary raw material through a variety of different processing schemes. The intermediate chemicals may be low-boiling hydrocarbon compounds such as methane, ethane, propane, and butane or higher-boiling hydrocarbon mixtures such as naphtha, kerosene, or gas oil. In the latter cases (naphtha, kerosene, and gas oil), these fractions are used (in addition to the production of fuels) as feedstocks for cracking processes to produce a variety of petrochemical products (e.g., ethylene, propylene, benzene, toluene, and the xylene isomers), which are identified by the relative placement of the two methyl groups on the aromatic ring: in the Also, by way of definition, petrochemistry is a branch of chemistry in which the transformation of petroleum (crude oil) and natural gas into useful products or feedstock for other process is studied. A petrochemical plant is a plant that uses chemicals from petroleum as a raw material (the feedstock) are usually located adjacent to (or within the precinct of) a petroleum refinery in order to minimize the need for transportation of the feedstocks produced by the refinery. On the other hand, specialty chemical plants and fine chemical plants are usually much smaller than a petrochemical plant and are not as sensitive to location.
Furthermore, a paraffinic petrochemical is an organic chemical compound, but one that does not contain any ring systems such as a cycloalkane (naphthene) ring or an aromatic ring. A naphthenic petrochemical is an organic chemical compound that contains one or more cycloalkane ring systems. An aromatic petrochemical is also an organic chemical compound but one that contains, or is derived from, the basic benzene ring system.
Petroleum products (in contrast to petrochemicals) are those hydrocarbon fractions that are derived from petroleum and have commercial value as a bulk product. These products are generally not accounted for in petrochemical production or used in statistics. Thus, in the context of this definition of petrochemicals, this book focuses on chemicals that are produced from petroleum as distinct from petroleum products, which are organic compounds (typically hydrocarbon compounds) that are burned as a fuel. In the strictest sense of the definition, a petrochemical is any chemical that is manufactured from petroleum and natural gas as distinct from fuels and other products, which are derived from petroleum and natural gas by a variety of processes and used for a variety of commercial purposes.
Petrochemical products include such items as plastics, soaps and detergents, solvents, drugs, fertilizers, pesticides, explosives, synthetic fibers and rubbers, paints, epoxy resins, and flooring and insulating materials. Moreover, the classification of materials as petrochemicals is used to indicate the source of the chemical compounds, but it should be remembered that many common petrochemicals can be made from other sources, and the terminology is therefore a matter of source identification. However, in the setting of modern industry, the term petrochemicals, is often used in an expanded form to include chemicals produced from other fossil fuels such as coal or natural gas, oil shale, and renewable sources such as corn or sugar cane as well as other forms of biomass. It is in the expanded form of the definition that the term petrochemical is used in this book.
In fact, in the early days of the chemical industry, coal was the major source of chemicals (it was not then called the petrochemical industry) and it was only after the discovery of petroleum and the recognition that petroleum could produce a variety of products other than fuels that the petrochemical industry came into being. For several decades both coal
and petroleum served as the primary raw materials for the manufacture of chemicals. Then during the time of World War II, petroleum began to outpace coal as a source of chemicals—the exception being the manufacture of synthetic fuels from coal because of the lack of access to petroleum by German industry. To complete this series of definitions and to reduce the potential for any confusion that might occur later in this text, specialty chemicals (also called specialties or effect chemicals) are particular chemical products, which provide a wide variety of effects on which many other industry sectors rely. Specialty chemicals are materials used on the basis of their performance or function.
Consequently, in addition to effect chemicals they are sometimes referred to as performance chemicals or formulation chemicals. The physical and chemical characteristics of the single molecules or the formulated mixtures of molecules and the composition of the mixtures influence the performance of the end product.
On the other hand, the term fine chemicals is used in distinction to heavy chemicals, which are produced and handled in large lots and are often in a crude state. Since their inception in the late 1970s, fine chemicals have become an important part of the chemical industry. Fine chemicals are typically single, but often complex pure chemical substances, produced in limited quantities in multipurpose plants by multistep batch chemical or biotechnological processes and are described by specifications to which the chemical producers must strictly adhere. Fine chemicals are used as starting materials for specialty chemicals, particularly pharmaceutical chemicals, biopharmaceutical chemicals, and agricultural chemicals.
To return to the subject of petrochemicals, a petroleum refinery converts raw crude oil into useful products such as liquefied petroleum gas (LPG), naphtha (from which gasoline is manufactured), kerosene from which diesel fuel is manufactured, and a variety of gas oil fractions—of particular interest is the production of naphtha that serves as a feedstock for several processes that produce petrochemical feedstocks (Table 1.4). However, each refinery has its own specific arrangement and combination of refining processes largely determined by the market demand.
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Minerals Processing
Mineral processing is a form of extractive metallurgy that separates valuable minerals from the ore into a concentrated, marketable product. Mineral processing is also known as mineral dressing.
Mineral processing is conducted at the site of the mine and is a highly mechanical process, with oversight from a central control room.
The profitability of a mine is based on how much concentrate of the desirable mineral can be extracted from the ore. As a result, mineral processing is designed to yield the maximum amount of mineral concentrate possible before products hit the market.
If the case cannot be made for profitable yields of valuable minerals, then a mine will not hit the development stage in the lifecycle of a mine.
Mineral processing is used to extract the following materials:
Metals, including aluminum, bauxite, chalcopyrite, chromite, copper, galena, gold, hematite, iron, lead, magnetite, molybdenum, nickel, platinum, silver, sphalerite, tin, and zinc
Rocks, including including building stone, coal, clay, granite, limestone, potash, marble, and sand
Industrial mineral ore, including apatite, barite, diamond, fluorite, garnet, gemstones, quartz, vermiculite, wollastonite, and zircon
Mineral processing is an important step in converting ore into a product that can be sold and used for everyday applications.
What Are the 4 Stages of Mineral Processing?
Aside from profitability, the main objective of mineral processing is to break down ore from its heterogeneous properties and turn it into a homogeneous product to sell. To do this, materials will undergo the following four stages of processing to extract the desired crude material:
- Crushing and grinding. Crushing and grinding, also called comminution, is the process of reducing the particle size of large rocks to be further processed down the line, mineral-processing-wet-grinding-mill Wet grinding mill
- Sizing and classification. Sizing and classification is the process of separating different sizes of ore by screens. Finer materials are routed to different stages of the mine than coarser materials.
- Concentration. Concentration is the process of breaking down the materials until the desired concentration of crude material is reached. There are several different techniques for accomplishing the target concentration including:
Automated ore sorting. Automated ore sorting uses optical sensors to sort the rock into categories. This technology is expanding to include more sensing parameters.
Electrostatic separation. Electrostatic separation consists of electrostatic separators and electrodynamic sensors, also known as high tension rollers. Since these separators rely on electric currents, ore material needs to be dry. Charges are run through the materials and separate from the gangue—the undesirable ore that is removed from the profitable minerals. These separators are used to separate mineral sands.
Froth flotation. Froth flotation uses a chemical collector and frother that forms bubbles on the surface of the slurry that hydrophobic materials bind to. The bubbles are collected off the surface of the frother. Activators are used to enable the flotation of one mineral ore while depressants are used to inhibit the flotation of the gangue. Mineral-processing-flotation-bathFroth flotation tank
Gravity separation. Gravity separation is the process of separating two or more ore minerals in their respective responses to gravity paired with buoyant forces, centrifugal forces, and/or magnetic forces in a viscous substance.
Magnetic separation. Magnetic separation is the process of using electromagnets to extract the desired mineral ore from a conveyor belt. This process can be used with or without water.
- Dewatering. Dewatering is the final process of removing the water content of the mineral in order to dispose of the gangue and reach the desired concentrate levels for marketability.
Mineral Processing Equipment
Below is a list of equipment used at each stage of mineral processing:
Crushing and grinding equipment
Cone crushers
Gyratory crushers
Jaw crushers
SAG mill grinders
Rod mill grinders
Ball mill grinders
Pebble crushers
Sizing and classification equipment
Bar screens
Banana screens
Fine screens
Flip flop screens
Grizzlies
Multi-deck screens
Radial sieves
Vibratory screens
Wedge wire screens
Wire mesh screens
Fluidized classifiers
Spiral classifiers
Gas cyclones
Hydrocyclones
Ore sorters
Rake classifiers
Rotating trommels
Concentration equipment
Cleaners
Recleaners
Roughers
Scavengers
Dewatering equipment
Dewatering screens
Thickeners/clarifiers
Belt press/membrane filter press
Fluidised beds
Hearth dryers
Rotary dryers
Rotary tray dryers
Spray dryers
Mixers and Agitators (Turbulator)
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Industrial Effluent Control
Rapid industrialization and urbanization are becoming the new fulcrum for a nation’s economic growth and a critical area for human well-being. But it is also becoming an emerging point-source of water pollution and a decisive, inescapable, threat to disturb the ecosystem and homeostasis of the environment. The released industrial effluents are contributing majorly to water pollution.
Moreover, the release of inefficiently treated effluents into the rivers and the degraded quality and quantity of the available groundwater are majorly depleting the consumable drinking and domestic water supply. Henceforth, water, a critical environmental abiotic factor, is heavily stressed and polluted with a diverse array of industrial effluents. It needs to be treated and protected whilst demanding sustainable industrial effluent treatment models. Industrial effluents are broadly categorized into three categories depending on the type of manufacturing industry,
1) inorganic process waste (chemical industry)
2) organic process waste (textile, food processing, dairies, breweries, and chemical industries)
3) chemical waste (fertilizers, insecticides, dyes, acids, bases, and raw material manufacturing industries). Among the effluent waste, the organic component is more problematic and challenging in remediation.
Notably, some effluents are hazardous, toxic, and fatal owing to their non-biodegradable and persistent physical-chemical properties. Talking about their composition, they are highly diverse in terms of the concentrations of various standard parameters. For example, a pH range of 5–12 exhibits higher biochemical oxygen demand (BOD, 100–3000 mgO2/L) and chemical oxygen demand (COD, 10–2250 mgO2/L).
Certainly! Industrial effluent control is a critical aspect of environmental protection. Let’s delve into the basics:
Understanding Water Chemistry:
Water has fascinating properties, especially its ability to solubilize substances into ions. The concentration of hydrogen ions in water determines its pH, which ranges from 0 (very strong acid) to 14 (very strong alkali). A pH of 7 indicates neutrality.
For discharging treated effluent into the environment, the pH must fall within acceptable ranges (usually pH 5 to pH 9) to avoid harming aquatic life.
Strong acids (e.g., hydrochloric acid) are highly dissociated in solution, while weak acids (e.g., acetic acid) have fewer hydrogen ions available.
Industrial Effluent Treatment Plant:
Designing an industrial effluent treatment plant requires specialized knowledge. Chemical engineers should understand the discipline’s basics to discuss it intelligently with designers and suppliers.
Key unit operations in an industrial effluent treatment plant include:
Physical Processes: Screening, sedimentation, and filtration.
Chemical Processes: Coagulation, flocculation, acid neutralization with lime and chemical precipitation.
Biological Processes: Aerobic and anaerobic treatment.
Terminology used by water specialists includes terms like BOD (biochemical oxygen demand), COD (chemical oxygen demand), and TSS (total suspended solids).
Biological oxygen demand (BOD), also known as biochemical oxygen demand, is an analytical parameter that represents the amount of dissolved oxygen (DO) consumed by aerobic bacteria growing on the organic material present in a water sample.
The Turbulator Aeration Units are widely used to assist in the increase of (DO) to effectively reduce B.O.D. and C.O.D. concentration. These units are typically mounted on concrete/steel structures, or they are mounted on rafts to enable the movement of these units for optimal performance. Typical (DO) was demonstrated where transfer rates of 8-12ppm was recorded by Golder and Associates Consulting Engineers and Violia Water South Africa.
Measurement: BOD is typically expressed in milligrams of oxygen consumed per liter of sample during 5 days of incubation at 20 °C. During this period, aerobic bacteria metabolize the organic compounds, consuming dissolved oxygen in the process.
Purpose: BOD analysis is commonly used as a surrogate indicator of organic water pollution. It helps gauge the effectiveness of wastewater treatment plants by measuring the impact of effluents on the oxygen levels of receiving water bodies.
Comparison with Chemical Oxygen Demand (COD): While both BOD and chemical oxygen demand (COD) analyze organic compounds in water, BOD is more specific because it measures only biologically oxidized organic matter. In contrast, COD measures everything that can be chemically oxidized, including both biologically and non-biologically oxidizable substances.