Difference between revisions of "Environmental concerns"

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[[File:solid_wastes.png|frame|center|'''Table 1:''' Solid waste treament]]
 
[[File:solid_wastes.png|frame|center|'''Table 1:''' Solid waste treament]]
  
Table 1 shown above introduces several forms of solid waste disposal. The main types of disposal are recycling, chemical conversion, incineration, pyrolysis, and landfill.<ref name="peters" /> Chemicals can be recovered from solids through extraction or stripping, while valuable solids can be recovered through a variety of methods such as flotation, electrical conductivity, or hand picking. Recycling these products or even selling them can often save company money in the long run. Chemical conversion of solid waste can often be used to convert the waste into something less harmful or sellable. Incineration is used to create a residue that is much smaller and more acceptable for landfill application.  Incineration can be expensive, but if done properly can potentially recover some fuel value through the generation of steam. Pyrolysis, or the heating of the waste in an air-free chamber, is an alternative to incineration that avoids a lot of the air pollution issues associated with incineration.<ref name="peters" />
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Table 1 shown above introduces several forms of solid waste disposal. The main types of disposal are recycling, chemical conversion, incineration, pyrolysis, and landfill.<ref name="peters" /> Chemicals can be recovered from solids through extraction or stripping, while valuable solids can be recovered through a variety of methods such as flotation, electrical conductivity, or hand picking. Recycling these products or even selling them can often save company money in the long run. Chemical conversion of solid waste can often be used to convert the waste into something less harmful or sellable. Incineration is used to create a residue that is much smaller and more acceptable for landfill application.  Incineration can be expensive, but if done properly can potentially recover some fuel value through the generation of steam. Pyrolysis, or the heating of the waste in an air-free chamber, is an alternative to incineration that avoids a lot of the air pollution issues associated with incineration,<ref name="peters" /> as the pollutants produced are contained and can be treated. Figure 11 shows pyrolysis of solid waste.
  
Landfills are useful for disposing large quantities of waste, but if the contents are legally classified as "hazardous", the waste must go through a pretreatment process in order to reduce the contaminants to an acceptable level. Additionally, proper lining of the landfill must be installed to prevent leachates that seep from the landfill and into groundwater.
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[[File:Pyrolysis.png|frame|center|upright=2|'''Figure 11:''' Pyrolysis of solid waste <ref> Arc21 ''Energy from Waste (EfW)'' http://www.arc21.org.uk/opencontent/?itemid=27&section=Residual+Waste+Project </ref>]]
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Landfills are useful for disposing large quantities of waste, but if the contents are legally classified as "hazardous", the waste must go through a pretreatment process in order to reduce the contaminants to an acceptable level. Additionally, proper lining of the landfill must be installed to prevent leachates that seep from the landfill and into groundwater. With the proper set-up, landfills can be used as a source of methane gas. A landfill diagram depicting both the lining requirements and a methane collection system is shown below in Figure 12.
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[[File:Landfill.png|frame|center|'''Figure 12:''' Landfill <ref> Ohio Wesleyan University - Environmental Geography ''Landfill Facts'' http://www.arc21.org.uk/opencontent/?itemid=27&section=Residual+Waste+Project </ref>]]
  
 
=Waste Minimization=
 
=Waste Minimization=

Revision as of 22:03, 26 February 2015


Authors: Sean Cabaniss, [2014] David Park, [2014] Maxim Slivinsky, [2014] Julianne Wagoner, [2014] and Michelle Spiezio [2015]

Steward: David Chen, Jian Gong, and Fengqi You

Date Presented: Feb. 23, 2014


Contents


Overview

All industrial processes produce waste in some form that must be carefully handled and disposed of according to regulations set down by governments at varying levels. The key areas for consideration are emissions to the air, water, and land, smells, noise, and visual impact, and waste management. It is important to remember that pollution considerations are both a moral and legal obligation for any engineer or industry. [1] Emissions from chemical plants are regulated by both local and federal governments. Plants are required to monitor and document waste streams discharged to the environment, maintain permits from local governmental agencies, and either pay fines or directly address any violations.[2] Waste management can come in many forms to minimize the impact on the environment. Some key strategies include dilution and dispersion of the harmful chemicals, discharge into foul sewer water with permission from the appropriate authorities, physical treatment methods, chemical treatments, biological treatments, incineration, landfill at controlled sites, and dumping into the sea.


Human Health, Social and Economic costs

Environmental concerns associated with process plants encompass more than just air, land, and water pollution. There are also a variety of other indirect costs that should be considered, as they too can have a large impact on both the environment and company profit if not properly addressed. These costs are directly linked to all the types of pollution that a plant releases. Whether it is air pollution, water pollution, or even excess noise, it is important to minimize the impact of these discharges on the health of both the local community and the population as a whole, due to the far reaching effects of most types of pollution. Addressing pollution responsibly will also minimize social costs, those that are linked with how the public perceives the company. Being perceived positively by the public will minimize costs associated with having to boost company image and gain the trust of communities. Environmental stewardship also ties into economic costs. Having to pay for environmental compliance equipment may be expensive, but neglecting to do so will result in even larger legal fees and costs associated with cleaning up disastrous spills.

Human Health

The human costs associated with chemical plant pollution come in the form of endangerment to the health of people in local communities. Because chemical plants are not going to be fully contained, it is necessary to determine how those streams and pollutants that are emitted affect the surrounding population. Figure 1 shows the various effects of pollution on the human body. A few examples of this are: contamination of the local potable water supply if, for instance, chemicals in a retention pond leech out and into groundwater; release of particulate matter reducing the air quality of a community to the point where instances of asthma increase; and, the release of hazardous chemicals causing carcinogenic effects.[3]

Figure 2 below shows the world wide impact of air and water pollution as it relates to the impact of infectious disease malaria. The number of premature deaths from pollution is obviously quite high, however WHO currently estimates that the numbers are ever higher. WHO now estimates 7 million deaths annually linked to air pollution. This large number comes from new data which suggests that there is a strong link between air pollution exposure and cardiovascular diseases and cancer. Air pollution is also the cause of numerous respiratory diseases. [4] Water pollution concerns that we hear about mostly have to do with biological pollutants, such as bacteria and parasites that cause illness. Water polluted with microorganisms causes 80% of all infectious diseases. [5] This, however, mostly comes from mistreatment of human waste, not from industrial pollution. Industrial chemical pollution is controlled by the EPA, thus the levels of chemicals industry can release into water is low enough to not cause any health issues in humans. However, there are still unknown health effects for a large number of chemicals.

Figure 1: Health Effects of Pollution [6]
Figure 2: Deaths Associated with Pollution [7]

Social

The social costs linked to environmental concerns relate to public perception of a company and its actions with regard to environmental stewardship, as well as the social impact on society. Any company that produces waste streams is going to be scrutinized by the public for the way these streams are handled. Companies caught or known for high pollution levels often receive bad press, which can also give investors a bad impression and hurt stock prices. It is to the advantage of the company, therefore, to prove to the public that every effort is being made to responsibly handle waste streams.

These costs can be the burden of both society and industry. In 2011, it is estimated by the NRDC that air pollution caused the loss of 3.4 million work days in the United States.[8] These lost work days combined with medical bills sum to a cost as high as $78 billion dollars. Social costs to industry can come in the form of money spent to improve company image. The amount varies based on situation, but can be very high, especially in the wake of an environmental disaster. A recent example of high social costs is the outcry in the wake of the BP oil spill. In 2012, BP and the Department of Justice reached a settlement where BP would pay $4.5 billion in fines. However, BP projects that the spill will cost around $40 billion due to all of the payments to not only settle claims, but to support efforts to rehabilitate the Gulf Coast ecosystems and businesses that (not mandated by the court). Additionally, BP has to work to continue to turn around the 35% reduction in stock prices since the spill. [9]

Economic

The main economic costs come from the installation and operation of environmental control equipment.[10] These costs are of separation equipment, such as settling tanks, electrostatic precipitators, and distillation columns, as well as disposal equipment, such as incinerators and reactors that neutralize or oxidize a waste stream. Another cost that companies must incur is that of the removal of these wastes. Companies will often pay third party waste management companies to take waste streams and dispose of them, through means such as burial and placing in a landfill, for example. There are also the costs of cooling towers and noise abatement measures to take into consideration. The cost of water treatment systems typically accounts for around 1.3% of fixed-capital investment, while waste disposal facilities cost up to 2% of fixed-capital investment. [11]

The cost of not taking the environment into consideration when designing a process can far outreach that of the equipment, however. If a company does not follow regulations, they incur legal expenses as a penalty. Additionally, failure to comply can a high cost associated with poor public perception of the company. Bad press and public protests can lead to a large loss in profit. [11] For example, just to avoid strict air standards that would impose costs of better pollution control equipment, power companies spent $67 million between 2010 and 2012 lobbying congress against clean air regulations. [8]

In the long run, it can often be in a company's best interest to take environmental factors into consideration. Optimizing a process, to reduce waste, results in less money that needs to be spent on waste disposal. Additionally, using recycle streams effectively may reduce the cost of the inputs to the process. Finally, if a process is designed in such a way that the waste streams are actually desired by another company, there is actual profit that can be made through the sale of this “engineering scrap.”[12]


Types of Pollution and Treatment

Environmental concerns associated with process plants encompass more than just air, land, and water pollution. There are also a variety of other indirect costs that should be considered, as they too can have a large impact on both the environment and company profit if not properly addressed. These costs are directly linked to all the types of pollution that a plant releases. Whether it is air pollution, water pollution, or even excess noise, it is important to minimize the impact of these discharges on the health of both the local community and the population as a whole, due to the far reaching effects of most types of pollution. Addressing pollution responsibly will also minimize social costs, those that are linked with how the public perceives the company. Being perceived positively by the public will minimize costs associated with having to boost company image and gain the trust of communities. Environmental stewardship also ties into economic costs. Having to pay for environmental compliance equipment may be expensive, but neglecting to do so will result in even larger legal fees and costs associated with cleaning up disastrous spills.

Noise Pollution

Noise pollution is any unwanted or disturbing sound that diminished quality of life.[13]

Causes & Effects

Equipment that are likely to be noisy are compressors, fans, burners, and steam relief valves.[1] Whereas this unwanted noise may often be considered just an annoyance, there are studies that link elevated noise to health issues. For example, being exposed to unwanted noise can lead to an increase in stress and disruption of sleep, thus leading to increased blood pressure. Exposure to high levels of sound can lead to Noise-Induced Hearing Loss (NIHL).[1] Sound is measured in decibels (dB) and is determined by the following expression:

 Sound\ level=20*\log_{10}(\frac{RMS\ sound\ pressure}{2E-5})

RMS sound pressure is equal to the localized change in atmospheric pressure caused by sound waves, measured in Pa. Sound meters determine noise level as a human ear would, providing measurements in dB(A) units. The “A” term corresponds to the weighting used by the meter to mimic the human ear. Permanent damage can be caused at sound levels above 85 dB(A), and ear protection is customarily worn in areas where levels are around 80 dB(A) and above. [14]


Treatment

To mitigate the adverse human effects of noise pollution, the EPA has included provisions in the Clean Air Act, the noise Control Act of 1972 and the Quiet Communities Act of 1978. However, the responsibility of noise control is mainly handled at the State and local level.[13]

Some design decisions can be made to reduce the effects of noise on humans. Noisy equipment should not be placed near rooms that are often occupied. Additionally, rooms can be insulated to mitigate the length which the noise travels. If workers are to be near noise, they should wear earplugs to reduce the impact. Finally, choosing a plant location that is far from communities will reduce the amount of people exposed to any loud noises.

Thermal Pollution

Alt text
Figure 3: Effects of Thermal Pollution [15]

Thermal pollution relates to the heat released by a plant into the environment. This often comes from water that was used to cool down a process and then released into the environment.

Causes & Effects

The largest concern with regards to thermal pollution is water quality. The temperature of water directly relates factors such as density, surface tension, and to the solubility of gases in the water. The most important consideration is the solubility of oxygen in water. Dissolved oxygen in water is essential in maintaining aquatic life. Thus changing the temperature of water due to thermal pollution can alter water ecosystems. An additional concern is that increased water temperatures lead to a reduction in capacity for organic wastes assimilation. Figure 3 shows a summary of the effects of thermal pollution on water systems.

Treatment

Because of the negative effects of thermal pollution, and federal water temperature standards, design engineers must employ the use of various process technologies to mitigate thermal pollution. Options for reducing temperatures of water streams are: cooling towers, cooling ponds, and spray ponds. All of these technologies use the principles of heat transfer across a water-air interface, thus the heat from the water is transferred to air, which can be released into the environment. Another consideration is to recycle the heat. Hot water or fluid waste/effluent streams can be used in a heat exchange network to transfer heat to an inlet stream that requires heating before entering a process.

Air Pollution

Air pollutants can be either gases or particulate matter suspended in an effluent air stream. Some examples are: CO2, sulfates, nitrates, particulates (PM10, PM2.5), Volatile Organic Compounds (VOC) and, less commonly, chlorine compounds.[1]

Causes & Effects

These pollutants often come from fired heaters, boilers or flares. These wastes are often under careful scrutiny from governments as well as the public since gases being released from towers are often the easiest forms of pollution for a casual observer to see.

Emissions to the air can be particularly dangerous because, if left unchecked, they can have far reaching consequences. Historically, the focal points for air emissions have been the effects on acid rain, ozone and greenhouse gases. Lately, greenhouse gases have been the most scrutinized due to growing concerns of global warming.

Treatment

Air emissions must be treated before being released into the atmosphere, especially given the recent emphasis on green processes and the growing alarm with regards to global warming. Due to the properties of gases, air pollution control can be the most expensive and energy intensive. Typically, there are two main classifications of air pollution control equipment: those associated with removing gaseous pollutants from streams to be released into the air and those that can physically remove particles from these streams.

Equipment chosen to remove a gaseous pollutant depends on whether the gas is easily reacted into something that is less harmful to the environment. Noxious elements are often removed by absorption, using a gas scrubber which utilizes a liquid solvent, or by adsorption, using a gas adsorber utilizing either a liquid or solid as the adsorber for the pollutant being removed.[11] An important note is that these pieces of equipment often do not render the pollutant harmless, but simply change the form from gas to liquid or from gas to solid, both of which needs further treatment. For those pollutants which can be reacted into something less harmful, equipment such as reactors and incinerators are used. For example, combustible vapors are often burned in either a direct incinerator or in a catalytic incinerator, to increase the efficiency of the burning reaction. However, these incinerators often require very high operating costs.

Figure 4: Particulate Size and Corresponding Machinery

For the removal of particles from gas streams, there is a wide variety of possible equipment, chosen based on particle size and characteristics, as shown in Figure 4 above.[11] Mechanical collectors are generally used when particle sizes are large. Some mechanical collection equipment are: settling chambers, which are driven by gravity; cyclones, which make use of centrifugal forces; and bag filters, which collect particles from the gas by interception on the fabric surface of the bag.[13] Mechanical collectors are all dry methods of particle removal. There are also a variety of wet methods that can be employed to rid gases of particles. Wet methods such as a spray tower and Venturi scrubber rely on the collision of the particles with water to remove the particles from the gas, as seen in Figure 5. A final method of particulate removal is an electrostatic precipitator (ESP), Figure 6. An ESP will charge the particles in the gas by applying a high voltage, then allow these charged particles to be attracted to oppositely charged collection plates.[11] ESPs are useful for removing ultra-fine particles from corrosive gas streams, but are often sensitive to the properties of the particle. Additionally, the method of using rapping to remove the particles from the collection plates is rudimentary and often causes maintenance issues.[13]

Figure 5: Gas Scrubbing [16]
Figure 6: ESP [17]

Water Pollution

Types of water pollutants are: chemicals, such as oil; suspended solids, such as metals and biological materials; and dissolved (aqueous) materials, such as ions.

Causes & Effects

Alt text
Figure 7: Sources of water pollution [18]

Water pollution mainly comes from agriculture, urban runoff, and industry, as shown in Figure 7. Many of these chemical pollutants are regulated by the EPA, but there are still many that aren't. This is due to the fact that there simply is not comprehensive information on the effects of these chemicals to the environment and humans. For chemical engineering, industrial water pollution is the most applicable. This typically comes from three streams: process waste, utility waste and run-off streams. Process waste streams are the unwanted side products of reactions and include salt water, hydrocarbon contaminated water, biologically contaminated water, and water with too high or low pH. Utility waste is mainly produced from cooling tower water blowdown. The purpose of blowdown is to prevent a buildup of salts in the towers, but produces a stream of contaminated water. Finally, run-off streams come from rain water, hydrant flushing and equipment washing.

Liquid wastes are typically not as far reaching as gaseous waste, but can be much more devastating. Ecosystems can be destroyed from poor wastewater policies. Local populations can suffer from a lack of clean drinking water or dying wildlife in the area. The BP oil spill was a highly visible incident that showed how much damage can be done by water borne pollutants.

Aqueous wastes can be the most immediately harmful to the environment and people living nearby and must be sent immediately to an effluent treatment. Some of the most common, harmful water contaminants are ammonia, salts from deionizers, hydrocarbons, spent acids, caustics, and various forms of biological contamination. Utilities on-site can also create large wastewater flows that must be purged in order to prevent solid buildups. The most efficient way to deal with contaminated runoff is to collect and purify it on-site before disposing of it.[11]

Treatment

The main factors that usually have some sort of legislative constraints are pH levels, suspended solids, toxicity, and biological oxygen demand. Oxygen demand is often under looked as a form of pollution because there is rarely visible evidence that something is wrong in the stream. However, many local governments mandate that the water leaving a plant must have enough oxygen to sustain aquatic life before being released.

Liquid wastes are usually flammable and can be burned in an incinerator as long as care is taken to insure the temperatures are high enough to destroy the harmful compounds. This only shifts the problem, however, as it creates gaseous wastes.

Alt text
Figure 8: Rapid Sand Filter Schematic [19]

Wastewater that contains large particles, either floating or suspended, will usually be first treated by simply skimming off or pulling out the large masses of particles. Following this, wastewater will be sent to a sedimentation basin to allow the particles to settle due to the force of gravity. The sludge that forms on the bottom of the basin is removed with sludge scrapers. For smaller particles that are not settled out of the water, a rapid sand filter or multimedia (usually sand and anthracite) filter, shown in Figure 8, can be used.[20] For very small particles, membrane processes can be employed. These include ultra-filtration, which uses exclusion of particles based on size, reverse osmosis, shown in Figure 9, which excludes based on both size and particle properties, and electrodialysis, which is used to remove ionic species from the water.[11]

Figure 9: Reverse Osmosis Water Treatment [21]

To treat water contaminated with organic matter, microorganisms can be used. The microorganisms break down the organic matter, either aerobically or anaerobically depending on the organism. Aerobic biological processes either used activated sludge, shown in Figure 10, where biological growths are mixed in the wastewater and the resulting suspension is separated by gravity, or the fixed-film method, in which wastewater trickles over a biological film.[11]

Chemical treatment of water is generally used to remove color, odor, acids and alkalies, heavy metals, colloids, and oil. To remove colloids, coagulation is often used. In coagulation, chemicals are added to the water to break down the electrostatic double layer or the colloidal particles, essentially to neutralize the charge of the particles, allowing them to combine during flocculation.[20] To treat acid and alkaline waste, lime and sulfuric acid are often used.[11] Converse to this, distillation or salt precipitation methods can be used to recover the acid or alkali. To disinfect the water, chlorine or ozone are often used. Ozone, in addition to disinfection, is also useful for color, taste, and odor removal from the water.


Figure 10: Wastewater Treatment with Activated Sludge [22]

Land Pollution

Land pollution is any solid wastes that requires disposal. Solid wastes are generally identified as flammable, toxic, corrosive or reactive. Waste containing any of these characteristics must be specially handled to ensure as little damage to the local environment as possible.

Causes & Effects

Left unchecked, large amounts of flammable waste could ignite and become very difficult to control. Toxic, corrosive or reactive materials have averse affects to any local populations, often causing major health problems in humans and animals alike. Solid waste in a landfill can create chemical leachates which, if improperly handled, can seep into the ground and into groundwater.

Treatment

Solid, hazardous wastes are generally the easiest to control, but can also be the most difficult to safely discard; once created they can last much longer and do more damage than liquid or gaseous pollution. Table 1 below shows various types of solid wastes and how they can be treated.

Table 1: Solid waste treament

Table 1 shown above introduces several forms of solid waste disposal. The main types of disposal are recycling, chemical conversion, incineration, pyrolysis, and landfill.[11] Chemicals can be recovered from solids through extraction or stripping, while valuable solids can be recovered through a variety of methods such as flotation, electrical conductivity, or hand picking. Recycling these products or even selling them can often save company money in the long run. Chemical conversion of solid waste can often be used to convert the waste into something less harmful or sellable. Incineration is used to create a residue that is much smaller and more acceptable for landfill application. Incineration can be expensive, but if done properly can potentially recover some fuel value through the generation of steam. Pyrolysis, or the heating of the waste in an air-free chamber, is an alternative to incineration that avoids a lot of the air pollution issues associated with incineration,[11] as the pollutants produced are contained and can be treated. Figure 11 shows pyrolysis of solid waste.

Figure 11: Pyrolysis of solid waste [23]

Landfills are useful for disposing large quantities of waste, but if the contents are legally classified as "hazardous", the waste must go through a pretreatment process in order to reduce the contaminants to an acceptable level. Additionally, proper lining of the landfill must be installed to prevent leachates that seep from the landfill and into groundwater. With the proper set-up, landfills can be used as a source of methane gas. A landfill diagram depicting both the lining requirements and a methane collection system is shown below in Figure 12.

Figure 12: Landfill [24]

Waste Minimization

Chemical engineers need to keep several environmental considerations in mind when designing processes. During the design of the process, the toxicities of all the products, byproducts, and wastes produced by the system must be considered. Then, the reaction pathway that minimizes toxic components should be chosen whenever possible.[25] Emphasis must also be put on designing processes that operate at a nominal steady stare. Avoiding transient conditions, such as start-up or accidents, also avoids the production of excess waste.[25]

The general 5-step process for waste minimization can be summarized as: 1) Identify waste components for regulatory impact. 2) Identify waste streams for size and economic impact. 3) List the root causes of the waste streams. 4) List and analyze modifications to address the root causes. 5) Prioritize and implement the best solutions.[1] The hierarchy of waste management approaches is, as some are more effective than others, 10 source reduction, 2) recycling, 3) treatment, and 4) disposal.

When designing a process, emphasis should be placed on reducing the source of pollution in the first place. There are a variety of strategies for reducing that source of waste. Some of these are to reduce the concentration of impurities in feed streams, protect catalysts and adsorbents from poisoning and deactivation, and to eliminate the use of extraneous materials, such as solvents. Other strategies are to improve the efficiency of the process, by increasing recovery of separations because higher purity streams means smaller waste formation. Finally, altering background processes of the plant to be more efficient can save waste. For example, using a cleaner fuel as an energy source or a more environmentally friendly supplier reduces environmental footprint.[1]

A good design will seek to minimize, recycle, and make use of segregated waste streams in order to satisfy the demands of the waste market.[12] Optimization is a powerful tool for waste minimization because it cuts down on toxic materials as well as improving the overall system. Optimization can be used to account for environmental impact, such as the effects of carbon monoxide or other greenhouse gases. Recycling not only reduces the amount of waste, but also provides cost savings for a company. For example, recovering heat from wastewater can eliminate both thermal pollution and water pollution, while producing energy inputs if the suspended solids can be fermented to produce fuels. Processes should also be designed, if possible, to use materials that can are considered waste to other processes. If waste produced is considered a valuable product to another process, the waste can be sold or utilized, thus avoiding some of the costs associated with treatment and disposal.


Legislative Action

1972 Federal Water Pollution Control Act

The US Water Pollution Control Act set forth three major new regulations in an effort to keep toxic contaminants from getting into water supplies. Its goal was to achieve clean water for swimming, boating, and protecting fish and wildlife by 1983. This legislation said the EPA would set water quality standards for pollutants in surface water, set effluent guidelines for each industrial sector, and that it is unlawful to discharge any pollutant into navigable waters without a permit.[26]

Resource Conservation and Recovery Act (RCRA)

The ultimate goal of this act is to protect the groundwater from contamination. The act addressed waste management from "cradle to grave". It identified wastes on regulatory lists or if it has a certain characteristic level of flammability, toxicity, corrosivity, or reactivity. The act also specified how hazardous wastes must be labeled and tracked in transport as well as the treatments required for low levels of contaminants.[27]


Example Environmental Design Problem

Volatile Organic Compound Abatement[28]

The 1990 Clean Air Act mandates a reduction in emissions of volatile organic compounds (VOC). Any VOC emission sources exceeding 10tons/year must retrofit abatement processes with the best available control technology (BACT).

A paint spraying plant emits VOCs from vents in the paint spray booths. The stream contains primarily toluene, methyl ethyl ketone (MEK), and xylene, with small impurities of silicone and phosphorus. The concentration of VOCs in the dryer effluent varies between a minimum of 0.3 wt% VOC and a maximum of 1.2 wt% VOC with an approximate composition of 50% toluene, 25% MEK, and 25% xylene.

The painting company has commissioned you to evaluate three different technologies for a reduction in VOCs: thermal incineration, catalytic incineration, and carbon absorption and destruction of the VOCs. The low quality steam can be used by a nearby bottle washing plant.

Design an emission control plant for 50,000 scfm of vent gas at 100F and 25% relative humidity for 99% removal. The plant is located in Dearborn, Michigan, and the paint spray booths operate on a single 12-hour shift per day. Include the necessary start-up controls. The available fuel is natural gas or oil. Calculate the capital and operating cost and the $/lb or ton of VOC removed. Compare the three processes and recommend which is most suitable for this application.


Conclusion

Nearly all industrial chemical processes have pollution in one form or another. There are several sources and compounds of waste in all phases to be aware of and to know how to dispose of properly. A proper understanding of these hazardous compounds and materials as well as the effects these pollutants can have is essential, especially as an engineer. A chemical engineer's duty is to ensure that the waste, whether a gas, liquid, or sold is disposed of or recycled in a responsible manner and according to the local and federal guidelines. Proper waste management not only reflects well on a company and its engineers, but also can have lasting benefits to profits and the well being of locals in the area. On the other hand, reckless waste handling policies are not only dangerous for a plant and those around it, but are in danger of serious repercussions from the government and in the EPA. Finally, engineers have a moral obligation to uphold certain standards even when working in countries with less strict waste management standards.


References

  1. ^ a b c d e f Towler, G.P. and Sinnot, R. (2012). Chemical Engineering Design: Principles, Practice and Economics of Plant and Process Design. Elsevier.
  2. ^ Towler, G.P. (2012). Chemical Engineering Design, PowerPoint presentation.
  3. ^ EPA Website Health Effects of Air Pollution http://www.epa.gov/region07/air/quality/health.htm
  4. ^ WHO, 7 million premature deaths annually linked to air pollution, March 2014 http://www.who.int/mediacentre/news/releases/2014/air-pollution/en/
  5. ^ Environmental Pollution Centers, Water Pollution Diseases http://www.environmentalpollutioncenters.org/water/diseases/
  6. ^ Wikipedia web page,Pollution http://en.wikipedia.org/wiki/Pollution
  7. ^ Breath Project,Air Pollution World’s Top Killer by 2050 http://breatheproject.org/news/2012/03/
  8. ^ a b P. Altman The Price Of Pollution Politics: Eight Companies Attacking Clean Air Standards and the Toll on America’s Health NRDC: June 2012. http://www.nrdc.org/air/files/Price-of-Pollution-Politics.pdf
  9. ^ B. Skoloff, J. Wardell. BP Oil Spill Cost Hits $40 Billion, Company Returns To Profit Huff Post Green. http://www.huffingtonpost.com/2010/11/02/bp-oil-spill-costs-hit-40_n_777521.html
  10. ^ R.T. Turton, R.C. Bailie, W.B. Whiting, J.A. Shaeiwitz, Analysis, Synthesis, and Design of Chemical Processes, Prentice Hall: Upper Saddle River, 2003.
  11. ^ a b c d e f g h i j k M.S. Peters, K.D. Timmerhaus, Plant Design and Economics for Chemical Engineers, 5th Ed., McGraw-Hill: New York, 2003.
  12. ^ a b Seider, W.D. (2004). Process Design Principles: Synthesis, Analysis, and Evaluation, Wiley: New York.
  13. ^ a b c d G.D. Ulrich, A Guide to Chemical Engineering Process Design and Economics, Wiley: New York, 1984.
  14. ^ Wikipedia page, Sound Pressure http://en.wikipedia.org/wiki/Sound_pressure
  15. ^ Tutor Vista Effects of Thermal Pollution http://www.tutorvista.com/biology/effects-of-thermal-pollution
  16. ^ VITO,Gas scrubbing - general http://emis.vito.be/techniekfiche/gas-scrubbing-general?language=en
  17. ^ IHS GlobalSpec,Electrostatic Precipitators Information http://www.globalspec.com/learnmore/manufacturing_process_equipment/air_quality/electrostatic_precipitators
  18. ^ Environmental Working Group - National Drinking Water Database Drinking water pollution has many sources December 2009. http://www.ewg.org/tap-water/sourcesofwaterpollution.php
  19. ^ D. Schmitt, C. Shinault. Rapid Sand Filtration Virginia Tech Department of Civil Engineering, 1998. http://www.webapps.cee.vt.edu/ewr/environmental/teach/wtprimer/rapid/rapid.html
  20. ^ a b M.L. Davis, Water and Wastewater Engineering, Professional Edition, McGraw Hill: New York, 2010.
  21. ^ Hydrocomponents & Technologies Inc.,About Reverse Osmosis http://www.hcti.com/sm/aboutro/aboutro.html
  22. ^ ChemSearch,Biological Wastewater Treatment Systems https://www.chemsearch.my/bioamp/Pages/BiologicalWastewaterTreatment.aspx
  23. ^ Arc21 Energy from Waste (EfW) http://www.arc21.org.uk/opencontent/?itemid=27&section=Residual+Waste+Project
  24. ^ Ohio Wesleyan University - Environmental Geography Landfill Facts http://www.arc21.org.uk/opencontent/?itemid=27&section=Residual+Waste+Project
  25. ^ a b L.T. Biegler, I.E. Grossmann, A.W. Westerberg, Systematic Methods of Chemical Process Design, Prentice-Hall: Upper Saddle River, 1997.
  26. ^ U.S. Government page "Digest of Federal Resource Laws of Interest to the U.S. Fish and Wildlife Service" Digest of Federal Resource Laws of Interest to the U.S. Fish and Wildlife Service.
  27. ^ EPA Website "Resource Conservation and Recovery Act (RCRA)" http://www.epa.gov/agriculture/lrca.html
  28. ^ Robert Becker, Volatile Organic Compound Abatement, Environex, January 1994.