Public Health Engineering Sewerage, Second Edition

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Under such conditions the atmosphere is often highly irritating to the eyes and to the respiratory tract and is far too intense to be accounted for by the materials emitted to the atmosphere from the varying and separate sources. Research on this field has been extensive.

Manual on Sewerage & Sewage Treatment, 2nd Edition

Many theories are postulated with regard to this problem, but the consensus is that it is the photochemical action between oxides of nitrogen and unsaturated hydrocarbons from automobile exhaust gases combined with several products of health concern such as ozone, formaldehyde, and organic compounds of nitrogen that give rise to the condition. These substances can condense on particulate matter in the atmosphere to form fog.

Knowledge of chemistry helps very much in finding the root cause of this matter. Motor vehicles, factories, and power plants are the main contributors to air pollution. Such pollutants can cause cancer or other serious health effects, such as reproductive or birth defects, damage to the immune system, and respiratory problems, or they may cause adverse effects to the environment itself. The Clean Air amendments list toxic air pollutants that the U. S Environmental Protection Agency is required to regulate. These include particulate matter; halogen compounds such as tetrachloroethene, dichloromethane, and dioxin; heavy metals such as mercury, cadmium, and lead; volatile organic compounds such as benzene and toluene; and other hazardous compounds such as asbestos.

Building materials and furnishings are likely to include toxic chemicals that may be slowly released. Asbestos and radon, products used for household cleaning and maintenance, personal care, or hobbies often contain volatile can also cause serious harm. Usually the impact of human activities significantly cause problem in environmental quality.

Manual on Sewerage and Sewage Treatment Systems - 2013

Apparently, the human activities in one region have a significant impact and affected the quality of air at a much further region. This was true in the case of the radioactive fallout. Current concerns are on global warming and stratospheric ozone depletion. It is very important to grasp well the chemical principles involved to help us understand how these problems arise and how they could be solved. Because of this impact, chlorofluorocarbons are being banned from use globally and as such, replacement compounds are being sought. This reaction led to the phenomenon known as greenhouse gases.

Since they do trap heat trying to escape from the earth, they have potential for warming the earth, a process sometimes called global warming. Although there is a consensus on the reasons for increase on the concentrations of these gases, there is still an argument as to whether this will lead to a general increase in temperature. Much remains to be learned here, and the expanding knowledge on environmental engineering will enhance and contribute to a better understanding of this problem. It comprises legal matters on air, water, land and their impact on the environment.

Aspect and impact factors are very important and play a vital role in protecting our environment. It must be realised that human activities will somehow impinge on the surroundings. Activities in factories for instance, are directly associated with the pollution of the environment.

Factories producing paints discharge a lot of toxic substances and they will have to be dealt with properly to avoid the resultant negative impact to surroundings. Understanding of aspect and impact factors is a must for environmental engineers to meet the demand of sustainable development. As a result, we need clear guidelines to be closely followed in order to make sure our activities do not breach the existing laws and regulations.

The Environmental Quality Act allows the Ministry of Natural Resources and Environment after consultation with the Environmental Quality Council to define objectionable noise and to prescribe standards for tolerable noise. However, regulations with numerical limits of permissible noise are currently not available. Approval of such EIA and the projects usually include maximum permissible noise limits at the affected areas that must be complied with during the construction phase of a project, and upon operations of the projects plants, highway, etc.

EIA also requires us to measure the existing environment before a project starts. These include water quality, air quality, and the existing land condition. Therefore Environmental Quality Act is very important to be referred to before the development can commence. Legal compliance is very important when we implement a particular project and apply for certification. On chemical disposal for instance, there are clear guidelines on how to manage toxic wastes based on the relevant regulations. Industrial areas located near to water intake points must be strictly considered in accordance to the law and should comply with Standard A set out in the EQA Those factories situated away from water intake points must comply with the stipulated Standard B.

This is a clear message requiring us to control our water bodies based on the specified law and regulations. This act enables us to regulate open burning that gives rise to a serious problem in the form of haze to the environment. The most important thing that one has to understand is that open burning activities are prohibited by the law.

Environmental Quality Scheduled Wastes Regulations, Environmental Quality Clean Air Regulations, International Tropical Timber Agreement, , Geneva. Many of us are exposed to high levels of noise while at work, travelling, shopping, and where there can be intrusive noise from traffic, domestic appliances, and especially if you are living in badly constructed apartments or terraced homes, from your neighbours. In general, noise can be defined as unwanted signals.

To be more specific, noise is defined as unwanted sound. Therefore, noise can be considered as wrong sound at a wrong place and at a wrong time. Some people may find it tolerable, while others might find it annoying. Involuntary noise is noise that can be avoided. An example of involuntary noise is noise produced in a crowded area like a packed stadium. Voluntary noise is the noise which can be tolerated and the sufferer is normally being compensated.

For example, those who work at an airport have to tolerate aircraft noise. As such they are usually compensated with higher wages. In industrialized countries, noise is increasingly an environmental nuisance. It can interfere with human communication and sleep. Noise can also reduce the value of properties, e. Noise can also result in both physiological and psychological effects.

Extremely loud and sudden noises cause pain to the ears and may cause temporary deafness or permanent damage to our hearing. High noise level of sufficient duration can result in temporary or permanent loss of hearing. Prolonged exposure to noises which are not extremely loud can also affect hearing to a certain extent. Dangerous levels of noise come from industrial activities. Environmental noise intrusions such as traffic noise can interfere with communications, sleep disturbance and interfere with the ability to perform complex tasks.

If the noise starts to spread out from air, it is called air-borne. If the sound starts from vibration between structures, it is caused structure-borne. The structure-borne noise occurs when building elements are in direct contact with the noise source. Sound waves are characterized by their frequencies, amplitudes and phases.

The quality of a sound is determined by its frequency. For people with good hearing, the audible range of frequencies is normally between 20 Hz and 20, Hz. In most practical noise control problems, however, it is possible to consider a rather narrower range of frequency, say 50 Hz to 10, Hz. Sound with frequency less than 20 Hz is called infrasound and sound over 20, Hz is called ultrasound. However, most sound are not pure sinusoidal waves. They vary both in frequency and amplitude over time. To quantify their magnitude over the measured time T, the r.

For a point source, the noise is non-directional, and can be assumed as a spherical sound source. For a spherical sound source, the sound intensities at all points on the imaginary sphere surface are equal. In an environment in which there are no reflecting surface, the r. Therefore, sound pressure of linear scale is an inconvenient way to represent these quantities is to use logarithmic scale. An appropriate reference quantity is required. As sound level is expressed in logarithm scale, they cannot be added directly.

For quick estimation, table or figure can be used for addition of sound level. The Leq is a single value rating which has the same energy content as the varying sound level. As an example, sound pressure level cannot be used as an indication of loudness because the frequency of sound has quite a bit to do with how loud is the sound. For this reason, it is important for us to know the frequency of the noise we are measuring.

This contributes to the weighting networks. Weighting networks are electronic filtering circuit built into the meter to attenuate certain frequencies.

Sewage Is Helping Cities Flush Out the Opioid Crisis

They permit the sound level meter to respond more to some frequencies than to, something prejudicial like that of the human ear. The main different between these 3 networks are a very low frequencies are filtered quite severely by the A network, moderately by the B network, and hardly at all by the C network. Therefore, if the measured sound level of a noise is much higher on C weighting than on A weighting, much of the noise is probably of low frequency. When the weighting network is used, the sound level meter electronically subtracts or adds the number of the decibels shown on each frequency from or to the actual sound pressure level at that reading.

What is the corresponding SPL in dB? Example 2. What is the total SPL. Solution: By using Table 2. What is the equivalent continuous equal energy level for the 40 minutes period? Assume 5 minute sampling interval. While the saw is idle, it produces a level of 90 dBA at his work position. When it cuts into timber, it produces a level of 95 dBA. An exposure of 8 hours per day is assumed. It carries both the sound pressure level and frequency. This follows from the variation in sensitivity of the ear with frequency. For this reason, measurement of SPL in dB is not a very accurate measure of loudness.

The ear is not equally sensitive to all frequencies. Sound entering the ear is continuously frequency-analyzed along the cochlear partition, acting as a number of narrow band filters. The ear is most sensitive from Hz to Hz. The units used to label the equal- loudness are called phons. Since the ear is most sensitive to frequencies in the range 1 to 5 Hz, sound at these frequencies would be rate much louder than one at the same SPL at other frequencies.

The A weighting network is the most important network. The unit is dBA. However, the dBA is a single figure rating. It does not provide information on the frequency content of a noise source. It is recommended that type I instruments be used for industrial measurements and for environmental measurements involving legislation. A new IEC will replace the above standards. One major change is the abolishment of Type 3 noise meter. Fluctuations in level are common and sometimes the variations can be quite large.

It is most suitable for workers that move between many different environments during the working day. If D is greater than 1, the exposure has exceeded the permissible limit. In this respect, regulations with numerical limits of maximum permissible noise are currently not available. Whilst regulations with prescribes noise limits are not legally defined the Department of Environmental had issued guidelines on permissible noise limits in its course of enforcement of the Environmental Quality Act.

The noise limits that are often used are tabulated in Table 2. The guidelines for Siting and Zoning of Industries also give daytime and night time noise limits based on maximum sound levels according to the category of the industries. This requirement must be strictly adhered to at noise sensitive areas such as hospitals and schools. Approval of such EIA and the projects usually include maximum permissible noise limits at the affected areas that must be complied with during construction phase of the projects and upon operations of the projects i. Noise limits similar to that tabulated in Table 2.

There are provisions in the Environmental Quality Act for the control of sound propagated to the environment, affecting the community. The Department of Environmental is currently preparing guidelines for environmental noise control. These guidelines could then be enforced under the Environmental Quality Act and would be used in Environmental Impact Assessments, by the local authorities, and for planning proposes. Noise measurement and assessment procedures are to be also included. For example, there were sites in ancient Rome which were pits where carcasses, animals and humans, were dumped.

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Cities from the Bronze Age such as Troy were actually raised in levels as garbage became unbearable. Clay layers were spread over the garbage, just as in modern tips. Scavenging was one of the first forms of recycling and "rag and bone men" such as Steptoe and Son were just recyclers. The idea of scavenging was so bad to society that in the City of London outlawed the practice which is now an important part of the waste management industry. Historically, links between wastes and health have been another important catalyst for change.

A study in the mid 19th century demonstrated a link between sewage disposal in the Thames River and the incidence of cholera epidemics. This was 30 years before the cholera bacteria were even identified. Some of the earliest waste disposal schemes were established in order to escape the health problems associated with the industrial revolution including the development of garbage collection, street cleaning, and sewage collection schemes.

Another early waste treatment which moved from Europe to USA was to stew garbage and dead animals in large vats. This produced grease and 'residuum' which was a black gooey material. The grease was used for the manufacture of candles, soap, lubricants etc, and the 'residuum' was used as plant fertiliser.

The other wastes from this process were runoff into streams. This process was stopped in Europe in the 's but continued in the USA until the 's. Incinerators were developed in the s in England, and with the industrial development incinerator technology improved. Waste management in Malaysia displays an array of problems, including low collection coverage on average due to the inaccessibility by vehicles of some areas, irregular collection services, inadequate equipment used for waste collection, crude open dumping and burning without air and water pollution control, inadequate legal provisions and resources constraints.

These problems are caused by various factors which have an impact on the development of effective waste management systems in Malaysia. Institutional constraints are among these problems.

Even though several agencies like the State Department of the Environment and municipal councils are involved in waste management, they often have no clear functions in relation to waste management and there is no single agency designated to coordinate their projects and activities. The lack of coordination among the relevant agencies often results in duplication of efforts in waste management, wasting of resources, and un-sustainability of overall waste management programmes.

In the developing countries, waste management is becoming an acute problem as urbanization and economic development increase leading to larger quantities of waste materials requiring management in these countries. In Asia, the management of waste materials requires immediate attention especially in countries such as China, South Korea and Malaysia which have been categorized as emerging industrialized countries.

In , the urban areas of Asia produced about , tons of municipal solid waste MSW or approximately 2. In , this figure is estimated to increase up to 1. Table 3. Countries with low incomes have the lowest waste generation rates, averaging 0. High income countries such as Korea, Hong Kong, Singapore and Japan, tend to have higher waste generation in comparison to other countries.

In Hong Kong, the generation rate is among the highest due to intense construction and demolition within the municipality WB, The amounts of waste in Japan and Singapore are lower but that is also due to the fact that the data do not include all municipal waste generated within these countries. The characteristics of MSW vary from one country to another and the solid wastes of rural towns in Asia are significantly different from those of large cities, having more organics but few plastics from packaging or food wastes UNEP, There are also varying legal definitions of waste leading to differences in what is considered to be waste.

In general, waste is defined as any material which is unwanted by the holder and intentionally thrown away for disposal. This does not exclude that certain wastes may eventually become resources valuable to others once they are removed from waste stream WB, Malaysia, with a population of 24 million, is facing an increase of the generation and accumulation of waste.


This development is causing social, economic and environmental problems at a significant level. Individuals, industries, municipals, state and federal governments are concerned because improper waste management leads to health problems for local communities. Moreover, poor visual appearance has negative impacts on official visits and tourism. These problems are particularly serious in areas where intensive urbanization and population concentration lead to an increase of solid wastes and to a decrease of available land suitable for disposal.

May Malaysia, like most of the developing countries, is facing an increase in the generation of waste and of accompanying problems with the disposal of this waste. Overall, the local communities generate 16, tons of domestic waste per day and the amounts per capita vary from 0. On average, waste generation is about 1 kg per capita per day GAIA, Waste is grouped into three different categories in respect of disposal —solid waste, medical waste and hazardous waste.

According to a study by E. Incinerators were redesigned to allow more efficient energy production. At the same time there was an increasing awareness of environmental problems with a consequent upsurge in environmentally friendly practices including waste minimisation, waste recycling, and control of hazardous waste discharges.

One view of waste management is shown in the Figure The problem with this diagram is that it does not include waste minimisation or risk assessment procedures. These impinge on all the processes shown. This diagram also provides a framework for much of the material we will cover in Waste Technology. This refers to an arrangement or ranking of waste management actions which can usually be carried out in the community. At its simplest level you are probably familiar with "Reduce Reuse Recycle" This is a ranking of actions - we should reduce the amount of wastes produced as the first option.

The next option is to reuse what wastes are produced, e. The third option is to recycle material, e. This is depicted in Figure For example Figure shows a waste management strategy or hierarchy in which there has been a change from lower technology landfill disposal to higher technology recycling etc.

This has also led to an increase in waste minimisation. Source reduction ii. Recycling reuse and recycling wastes iii. Treatment - destroying, detoxifying or neutralising wastes iv. Disposal - discharging wastes. Other schemes utilise the 3 R's; Reduce, Reuse, Recycle. It can be seen that there is some overlap in these ideas - some common features, but they are very sketchy plans. When trying to plan waste management we are dealing with people, and planning any human activity is a complex process.

That is why we need to have relevant legislation. The term municipal solid waste MSW is often found in the literature. It generally implies all the wastes generated in a community with the exception of industrial process wastes and agricultural solid wastes. Waste composition is used to describe the individual components that make up a solid waste stream and their relative distribution, usually based on percentage by weight.

This is usually determined by a waste composition study. Waste composition is likely to change because of changes in lifestyle, increased recycling, education programmes, and changes in collection systems. Wastes are classified based on their composition. The National Waste Database Classification scheme should be used to ensure a standard approach. It does not include food processing wastes from canneries, slaughterhouses etc. Garbage originates mostly from domestic kitchens, stores, markets, restaurants etc Rubbish consists of combustible and non-combustible solid wastes from homes, stores and institutions but does not include garbage.

The term trash is often used in the same way but is probably more a subset of rubbish. The combustibles consist of paper, rags, wood, tree branches etc. Residential and commercial solid wastes, excluding special and hazardous wastes, consist of organic and inorganic solid wastes from residential areas and commercial establishments. Typically the organic wastes include food waste also known as garbage , paper, cardboard, plastics, textiles, wood, yard wastes etc. The inorganic fraction includes glass, metals - ferrous and non ferrous e.

If the waste components are mixed, then it's referred to as commingled MSW. Wastes that decompose fairly quickly, e. If we know how much waste is generated, we can then design management strategies to handle reduce, reuse, recycle etc those wastes. This sounds very good in principal, but the problem is we do not have very good figures on amounts of wastes being generated.

The actual composition of the wastes generated is another problem of definition. Figure shows the composition of the Malaysia domestic waste stream. For example, the recent waste audit in Muar showed that food wastes made up There are also variations over time as waste management has changed. Another important aspect of waste composition is the composition of recyclable material in MSW. Most of you are familiar with recyclable materials such as plastics, glass, metals etc. Substantial recycling is taking place in Malaysia which marks the future changes in waste composition.

This requires some sort of classification system. Classification is usually into hazardous and non hazardous classes, but could be extended to include recyclable versus non recyclable. Of the 12 tonnes of raw produce,10 tonnes become products,1. Stored separately, the damaged cans are recycled. Assume the materials separated for recycling and disposals are collected daily. Prepare a material balance for the cannery on this day and a material flow diagram accounting for all of the materials.

Also determine the amount of waste per tonnes of product. Solution: Step 1: On the given day, the cannery receives the following:- Step 2: As a result of internal activity:- - 10 tonnes of products are produced, 1. These are important for the management of waste disposal and for the recovery of a range of materials, including energy. It is important to note this information is distinctly important to determine the method of MSW disposal such as composting, landfills, recycling etc. The important physical properties of MSW include density sometimes referred to as specific weight , moisture content, particle size and distribution, field capacity, and porosity.

Density varies because of the large variety of waste constituents, the degree of compaction, the state of decomposition, and in landfills because of the amount of daily cover and the total depth of waste. Inert wastes such as construction and demolition materials may have higher densities, and density can change as in landfills where the formation of landfill gas and decomposition may bring about significant mass loss. Density is important because it is needed to assess the total mass and volume of waste which must be managed.

The density of MSW is often referred to as loose, as found in containers, un-compacted, compacted etc. Density varies not only because of the type of treatment it gets collection vs. Some typical density values are presented in the Table Moisture content is important in regards to density as above , compaction, the role moisture plays in decomposition processes, the flushing of inorganic components, and the use of MSW in incinerators.

Pre-treatment of waste to ensure uniform moisture content can be carried out prior to landfill disposal. For example, ferrous items which are of a large size may be too heavy to be separated by a magnetic belt or drum system. It is a critical measure because water in excess of field capacity will form leachate, and leachate can be a major problem in landfills.

Permeability depends on the other properties of the solid material including pore size distribution, surface area and porosity. This is especially important where wastes are burned for energy recovery, in which case the four most important properties are proximate analysis, fusing point of ash, elemental analysis, and energy content.

Elemental analysis is also important in determining nutrient availability. Some typical values are shown in Table Because of concern about halogens these are also often determined as well. The results of this analysis are used to characterise the composition of the organic matter in wastes. Typical values are shown in Table The energy content will be looked at later when discussing on incineration. Of most importance are the major nutrients in their various forms - nitrogen as nitrates, ammonium N phosphorus and potassium.

Using the data given in Table The most important biological characteristic of the organic fraction of MSW is that almost all the organic components can be converted biologically to gases and relatively inert organic and inorganic solids. The production of odours and the generation of flies are also related to the putrescible nature of the organic materials.

These will be discussed when talking about landfill processes. Solid wastes can be transformed by physical, chemical and biological means Table It can include such things as magnetic separation. The usual materials recovered include separation of recyclables, the removal of hazardous wastes, and the recovery of energy products.

Volume reduction refers to the processes whereby waste volumes are reduced, usually by force or pressure. Collection vehicles frequently have compaction mechanisms - or compaction can take place at a transfer station. The baling of plastics, paper, and aluminium is another means of volume reduction, as is the compaction that takes place in landfills.

Pressure can be used, e. Size reduction is used to reduce the size of wastes. It usually involves some form of shredding, grinding or milling. The main processes are combustion, pyrolysis, and gasification. Combustion is the chemical reaction with oxygen of organic materials accompanied by the emission of light and heat.

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These processes will be examined in more detail later in the course. When carried out anaerobically methane is produced - a typical component of landfill gas. This will be examined in more detail later. The different types of systems mentioned, not only for waste collection but also for the collection of recyclable materials is varied and governed by many factors some of which have nothing to do with waste management. It meant choosing the most appropriate trucks, designing collection routes, and then administering the collection.

With present day emphasis on recycling and composting the need to segregate materials has become most important. It can mean different vehicles collecting different material and taking it to different locations. As a result, the collection of wastes has become more complex and more expensive. To meet current needs there is a call for the development of an 'integrated collection strategy' which incorporates the following: i The system should provide locally appropriate levels of service, designed to meet political, health and regulatory requirements. Collection frequency may have to be altered because of weather conditions which can pose health and odour problems.

Increasing collection frequency has considerable cost implications and could lead to doubling of labour costs. Bins are placed near the curb side thus allowing the use of one-person vehicles with extending arms to collect the bins. In some locations, e. This means extra crews are required with extra labour costs. In some locations the crew actually come into the house yard often around the back to collect the bin.

This obviously slows collection times and increases costs. The use of centralised systems, such as apartment blocks, will accelerate collection times by reducing travelling distances and times. Each type has advantages and disadvantages and must also be related to the set out location.

For instance, large wheelie bins will be impractical in narrow urban areas with on-street parking. In New Zealand there is another advantage with bags in that in some districts a special sticker is required to be placed on the bag for costing purposes. Stickers can be easily seen by collection crews. The use of paper bags can provide advantages in composting in that they are easily shredded. The disadvantages of wheelie bin are one of size - most people put out more rubbish to fill the bin.

They also require mechanical lifting arms for health and safety reasons, and cost more initially. Interestingly, most wheelie bins are made out of recycled plastic. The set out location, size of area to be served, method of collection and costs of vehicles and operators are the major concerns. In most instances, curb side pickup is the most convenient, and the trend in recycling is towards some form of curb side pickup.

Drop-off and buy-back centre are not as convenient. Typically, a programme using such centre will have lower participation rates. Most communities and hauling companies face a dilemma in deciding how best to collect recycled materials, especially those with fleets of refuse vehicles. The prospect of replacing a fleet of refuse trucks with an equally expensive fleet of vehicles designed for recycling is normally not economically feasible, at least at first.

As a result, most recycling programmes try to use existing refuse equipment to collect recycled materials. Many innovative ideas have been used to convert refuse trucks to all-purpose refuse collection and recycling vehicles. For example, the city of Madison, Wisconsin, designed a newspaper rack welded to the frame of refuse trucks for the purpose of collecting bundled newspaper.

This low cost adaptation was first designed by city engineers in and is still in use today. The split-bin system in use in Byron Bay is a high-cost method, necessitation new bins and new collection vehicles. Benzenberg, F. Stearns, D. Cady Staley and Geo. Van Nostrand, Co. Chapter I: "Introduction" pp. PDF of insert. Chapter X: "Flushing and Ventilation" pp.

Patent for improvement in sewerage, Patented by W. West on June 4, Patent No. Thanks to Tom Bates for finding and contributing this patent. Patent for sewerage design, Patented by J. Crane on November 18, Patent for sewerage design - "Sewering and Draining Cities," Patented by George E. See Tracking Down the Roots for more information. Patent for sewerage design - "Sewering and Draining Towns," Patent for apparatus for removing sewage, Patented by I.

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Shone on December 28, Patent for sewer design, Comstock and T. Jefferson on July 11, The intent of W. PDF version - Pages Benzenberg, F. Stearns, D. Cady Staley and Geo. Van Nostrand, Co. Chapter I: "Introduction" pp.


PDF of insert. Chapter X: "Flushing and Ventilation" pp. Patent for improvement in sewerage, Patented by W. West on June 4, Patent No. Thanks to Tom Bates for finding and contributing this patent. Patent for sewerage design, Patented by J. Crane on November 18, Patent for sewerage design - "Sewering and Draining Cities," Patented by George E. See Tracking Down the Roots for more information. Patent for sewerage design - "Sewering and Draining Towns," Patent for apparatus for removing sewage, Patented by I.

Shone on December 28, Patent for sewer design, Comstock and T. Jefferson on July 11,