Environmental concerns: Difference between revisions

From processdesign
Jump to navigation Jump to search
No edit summary
Line 29: Line 29:


Table 3.1
Table 3.1
[[File:gas_pollutants.jpg]]
[[File:gas_pollutants.png]]

===Effects===
===Effects===



Revision as of 17:03, 23 February 2014


Authors: Sean Cabaniss, David Park, Maxim Slivinsky and Julianne Wagoner (ChE 352 in Winter 2014)

Steward: David Chen, Fengqi You

Date Presented: Feb. 23, 2014


Introduction

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 land, air, and water, waste management, smells, noise, and visual impact. It is important to remember that pollution considerations are both a moral and legal obligation for any engineer or industry [1]. Emmissions from chemical plants are regulated by both local and federal governments. Plants are required to monitor and document wate streams discharged to the environment, maintain permits from local governmental agencies, and either pay fines or directly address any violations [2].

Human, Social and Economic costs

There are several costs associated with pollution from chemical plants. Governmental regulations are in place in order to minimize the human costs of waste streams. These costs come in the form of endangerment or direct harm to local communities. The most obvious cases include poisoning drinking water or making air difficult to breathe. The United States government has tried to keep these factors under control, but the governments of other countries often try not to pass similar legislations in order to attract more business. In these cases, engineers can be forced to make an ethical decision on whether to minimize waste even if not required to by law.

Social costs are often linked to human ones and involve the public perception of the company. A recent example of high social costs is the outcry in the wake of the BP oil spill. Companies caught or known for high pollution levels often receive bad press, which can also give investors a bad impression and hurt stock prices.

The final cost involved with waste considerations is the economic costs. In the short run, it may often be more profitable to do as little as possible to mitigate waste. However, in the long run it can often be in a company's best interest to take these factors into consideration because an optimized process or a process that makes use of recycle streams effectively will produce less waste while also saving money for the company.

Impact

Gas

Causes & Pollutants

Gas pollutants often come from fired heaters, boilers or flares in the form of CO2 or other sulfates and nitrates, particulates (PM10, PM2.5), Volatile Organic Compounds (VOC) and, less commonly, chlorine compounds [1]. These gaseous 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. Various gas pollutatns and their sources can be found in table 3.1 below

Table 3.1 Gas pollutants.png

Effects

Liquid

Causes & Pollutants

Effects

Solid

Causes & Pollutants

Effects

Treatment

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.

Gas

Gaseous wastes 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 can be the most expensive and energy intensive. Noxious elements can often be removed by absorption or adsorption, which are the most common ways to treat gaseous wastes.

Liquid

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.

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.

Solid

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. 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 [3]. 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. 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].

Example Environmental Design Problem

Volatile Organic Compound Abatement [4]

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 absorbtion and destrcution 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.

References

  1. 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. Seider, W.D. (2004). Process Design Principles: Synthesis, Analysis, and Evaluation, Wiley: New York.
  4. E. Robert Becker, "Volatile Organic Compound Abatement", Environex, January 1994