ON-SITE STORAGE & PROCESSING. By P.MUTHURAMAN Assistant Professor Department of Civil Engineering, V V College of Engineering, Tisaiyanvillai.

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1 ON-SITE STORAGE & PROCESSING By P.MUTHURAMAN Assistant Professor Department of Civil Engineering, V V College of Engineering, Tisaiyanvillai.

2 On-site storage methods materials used for containers on-site segregation of solid wastes public health & economic aspects of storage options under Indian conditions Critical evaluation of options.

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9 The first phase to manage solid waste is at home level. It requires facilities for temporarily storing of refuse on the premises. Individual house holder or business man has responsibility for onsite storage of solid waste. There are four factors that should be considered in the on-site storage of solid waste. The type of container to be used, the location where the containers to be kept, public health, the collection method and time.

10 Proper container selection can save collection energy, increase the speed of collection and reduce crew size. Most importantly, containers should be functional for the amount and type of materials and collection vehicles used. Containers should also be durable, easy to handle, and economical, as well as resistant to corrosion, weather and animals. In residential areas, where refuse is collected manually, standardised metal or plastic containers are typically required for waste storage. When mechanised collection systems are used, containers are specifically designed to fit the truck-mounted loading mechanisms.

11 Efficiency, ( the containers should help maximise the overall collection efficiency.) Convenience, (the containers must be easily manageable both for residents and collection crew.) Compatibility, (the containers must be compatible with collection equipment. ) Public health and safety, (the containers should be securely covered and stored. ) Ownership, ( the municipal ownership must guarantee compatibility with collection equipment.)

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13 The design of an efficient waste collection system requires careful consideration of the type, size and location of containers at the point of generation for storage of wastes until they are collected. While single-family households generally use small containers, residential units, commercial units, institutions and industries require large containers. Smaller containers are usually handled manually whereas the larger, heavier ones require mechanical handling.

14 The containers may fall under either of the following two categories: (i) Stationary containers: These are used for contents to be transferred to collection vehicles at the site of storage. (ii) Hauled containers: These are used for contents to be directly transferred to a processing plant, transfer station or disposal site for emptying before being returned to the storage site.

15 The desirable characteristics of a well-designed container are low cost, size, weight, shape, resistance to corrosion, water tightness, strength and durability. Containers should not have rough or sharp edges, and preferably have a handle and a wheel to facilitate mobility. They should be covered to prevent rainwater from entering (which increases the weight and rate of decomposition of organic materials) into the solid wastes.

16 The container body must be strong enough to resist and discourage stray animals and scavengers from ripping it as well as withstand rough handling by the collection crew and mechanical loading equipment. Containers should be provided with a lifting bar, compatible with the hoisting mechanism of the vehicle. The material used should be light, recyclable, easily moulded and the surface must be smooth and resistant to corrosion. The steel and ferrous containers are heavy and subject to corrosion; the rust peels off exposing sharp edges, which could be hazardous to the collection crew. On the other, wooden containers (e.g., bamboo, rattan and wooden baskets) readily absorb and retain moisture and their surfaces are generally rough, irregular and difficult to clean.

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18 Generally, the containers used for waste storage are communal/public containers. The use of communal containers is largely dependent on local culture, tradition and attitudes towards waste. Communal containers may be fixed on the ground (stationary) or movable (hauled). Movable containers are provided with hoists and tails compatible with lifting mechanism of collection vehicles and such containers have capacities of 1 4 m^3.

19 In areas with very high waste generation rates, i.e., rates exceeding two truckloads daily, such as wet markets, large commercial centres and large business establishments, roll-on-roll or hoisted communal containers with capacities of m^3 and a strong superstructure with wheels are used. Normally, the collection vehicle keeps an empty container as a replacement before it hauls the filled container. It is advisable to place the containers m apart for economic reasons. The communal containers are usually staggered such that the effective distance of 100 m.

20 The major disadvantage of communal containers is the potential lack of maintenance and upgrading. The residuals and scattered solid wastes emit foul odours, which discourage residents from using the containers properly. In addition, if fixed containers are built below the vehicle level, the collection crew may be held responsible for sweeping and loading the solid wastes into transfer containers before being loaded into the collection vehicle. Sweeping and cleaning the communal containers of residuals obviously impose on the time of the crew members and take a longer time than if the wastes are placed in smaller containers.

21 To overcome the problem of maintaining communal containers, individual residents should maintain their own containers and locate them in designated areas. The communal area must have water and drains to facilitate the cleaning of the containers. This practice has the advantage of reducing the number of collection stops and at the same time maintaining the householder s responsibility for cleaning them. The residents must also be properly educated on the importance of good housekeeping.

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23 Galvanized metal containers Plastic containers Container liners Temporary and disposable containers(paper or plastic bags) Large portable or fixed containers Large open top containers enclosed storage containers containers equipped with self-contained compacting mechanism special containers that are sealed to carry toxic or radioactive wastes.

24 The most important factor in Onsite storage and handling of residential waste is that they are generated in areas with limited storage space. As a result they can have significant public health and aesthetic impacts. Public health concerns are related to the huge number of areas used for the storage of solid wastes with vermin and insects that often serve as potential reservoirs of disease. Aesthetic considerations are related to the production of odors and the unsightly conditions that can develop when adequate attention is not given to the maintenance of sanitary conditions.

25 The processing of wastes helps in achieving the best possible benefit from every functional element of the solid waste management (SWM) system. The purposes of processing (i) Improving efficiency of SWM system: I. Various processing techniques are available to improve the efficiency of SWM system. (ii)recovering material for reuse: Materials that can be recovered from solid wastes include paper, cardboard, plastic, glass, ferrous metal, aluminium and other residual metals. (iii) Recovering conversion products and energy: Combustible organic materials can be converted to intermediate products and ultimately to usable energy.

26 1) Component separation (hand sorting, screening, magnetic separation, air classification for lighter materials such as paper and plastic). It is much more efficient to separate wastes at the source. 2) Volume reduction (baling, shredding, incineration). Incineration may reduce volume by more than 90%. However, engineers should realize that incineration is not a popular option by many local communities. 3) Size reduction (Shredding, grinding) 4) Resource recovery (composting, energy recovery, material recovery)

27 OBJECTIVES 1. To recover recyclable or combustible materials as marketable by-products, 2. To reduce the levels of visible inert materials (e.g., plastics and glass), and 3. To reduce the levels of chemical contaminants (e.g., heavy metals and ). Component separation is a necessary operation in which the waste components are identified and sorted either manually or mechanically to aid further processing.

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29 Sl.No Technology Materials Targeted 1 Screening Large : film plastics, large paper, cardboard, Mid sized: recyclables, organic Fines: organic metal fragments 2 Hand Picking Recyclable, inert and chemical contaminants

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32 Screening is the most common form of separating solid wastes, depending on their size by the use of one or more screening surfaces. Screening has a number of applications in solid waste resource and energy recovery systems The most commonly used screens are rotary drum screens and various forms of vibrating screens. Most MSW composting facilities first convey the waste into a bag-opener and screen or trommel to separate different sizes of waste. Fine materials, including soil, grit, and much of the organic wastes, fall through the screen as "unders". Plastic films and large paper products are retained on the screen as "overs" and may possibly be recycled or marketed as a refuse derived fuel (RDF), which is burned for energy recovery.

33 Rotating wire screens with relatively large openings are used for separation of cardboard and paper products, while vibrating screens and rotating drum screens are typically used for the removal of glass and related materials from the shredded solid wastes. The efficiency of screen can be evaluated in terms of the percentage recovery of the material in the feed stream by using Equation. where U = weight of material passing through screen (underflow) kg/h; F = weight of material fed to the screen, kg/h; Wu = weight fraction of material desired size in underflow; Wf = weight fraction of material of desired size in feed.

34 With materials segregated to a relatively uniform size, it becomes much more practical to hand separate recyclables and contaminants as they move along conveyor lines. Previewing of the waste stream and manual removal of large sized materials is necessary, prior to most types of separation or size reduction techniques. This is done to prevent damage or stoppage of equipment such as shredders or screens, due to items such as rugs, pillows, mattresses, large metallic or plastic objects, wood or other construction materials, paint cans, etc.

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37 As materials are conveyed from one separation system to another, the conveyors can utilize magnetic belts, rollers or overhead magnets to separate the ferrous metals from the rest of the stream. Magnetic separation efficiency is sensitive to the depth of waste, as small ferrous items will not stick to the magnet if they are buried in non-ferrous materials, while larger ferrous items can drag non-ferrous items like paper and plastic along. A minimum of two stages of magnetic separation are usually needed to achieve efficient ferrous recovery. Magnetic separation is effective with iron and most steel, but does not separate aluminum, copper, and other non-ferrous metals. Consumer electronics can be difficult to separate magnetically, depending on the ratio of ferrous to non-ferrous materials.

38 Eddy current separation systems have been developed to separate non-ferrous metals. This technology works by exerting repulsive forces on electrically conductive materials. These systems should be located after magnetic separation to minimize contamination by ferrous materials. Aluminum is the primary metal recovered from MSW, although some copper and brass will also be separated. Cans literally jump off the conveyor into a waiting bin Eddy separators, while they do not achieve perfect removal of aluminum, do produce a relatively marketable aluminum by-product.

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40 This technique has been in use for a number of years in industrial operations for segregating various components from dry mixture. Air separation is primarily used to separate lighter materials (usually organic) from heavier (usually inorganic) ones. The lighter material may include plastics, paper and paper products and other organic materials. Generally, there is also a need to separate the light fraction of organic material from the conveying air streams, which is usually done in a cyclone separator. In this technique, the heavy fraction is removed from the air classifier (i.e., equipment used for air separation) to the recycling stage or to land disposal, as appropriate. The light fraction may be used, with or without further size reduction, as fuel for incinerators or as compost material.

41 In this type, when the processed solid wastes are dropped into the vertical chute, the lighter material is carried by the airflow to the top while the heavier materials fall to the bottom of the chute. The control of the percentage split between the light and heavy fraction is accomplished by varying the waste loading rate, airflow rate and the cross section of chute. A rotary air lock feed mechanism is required to introduce the shredded wastes into the classifier.

42 An experimental zigzag air classifier, shown in Figure, consists of a continuous vertical column with internal zigzag deflectors through which air is drawn at a high rate shredded wastes are introduced at the top of the column at a controlled rate, and air is introduced at the bottom of the column. As the wastes drop into the air stream, the lighter fraction is fluidised and moves upward and out of column, while the heavy fraction falls to the bottom. Best separation can be achieved through proper design of the separation chamber, airflow rate and influent feed rate.

43 These units are usually used to separate particles of glass, sand, and other heavy particles from organic materials prior to composting. A hammer mill or other size reducer is needed prior to wet separation to minimize the potential for air pockets in the heavy fraction. After entrainment in a circulating water stream, the heavy fraction drops into a sloped (and sometimes vibrating) tank where it moves to a removal zone. The less dense organic matter floats and is removed from the re circulating water using screening systems similar to those employed by wastewater treatment facilities. Wet separation is particularly effective at removing glass fragments and other sharp objects, which tend to be heavier than organic materials.

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45 Inertial methods rely on ballistic or gravity separation principles to separate shredded solid wastes into light (i.e., organic) and heavy (i.e., inorganic) particles. This method can be used in either initial processing or in the refinement of the final compost product. Compost is dropped on a rotating drum or spinning cone, and the resulting trajectory differences bounce glass, metal and stones away from the compost.

46 In the Bangalore city (India), the waste collected through street sweeping is the main system of primary collection of wastes. However, recently efforts are being made for doorstep collection of waste through NGOs (Non-Governmental Organisations) and private contractors, but only about 5% of the population is covered under this system. The waste generated by the rest is collected from either the street or the dustbins.

47 There are about 14,000 bottomless cement bins having 0.9 meters diameter and 0.6 cubic meter storage capacity and large masonry bins for depositing wastes at a distance of about 100 to 200 meters. Besides these, there are 1500 places, where the waste is deposited but no bins are kept on these sites. Recently, metal containers have been placed and at present 55 metal containers are in the city for the storage of waste in a more hygienic manner.

48 The frequency of removal of wastes varies from place to place, depending on the locality. Whichever system adapted in the area needs proper planning for collection, loading, unloading and transportation from transfer station and to the point of final disposal, considering traffic constraints, peak hour traffic, etc. An optimum collection schedule requires to be worked out where the number of premises or dumps is mentioned on a daily programme sheet, to be executed by the driver or supervisor in charge of collection. At present, it is estimated that there are about 4943 hotels/restaurants, which produce a large quantity of organic wastes in Bangalore.

49 Removal of garbage is a very important aspect of SWM, and the method of transportation is crucial. In essence, any breakdown in this system could create problems. Transportation implies conveyance from point of collection to the point of final disposal either directly or through a transfer system. In Bangalore, the transportation of waste is done by: engaging, departmentally, 82 trucks of the Corporation. engaging 129 vehicles, on contract, for layout and markets and 72 vehicles for transportation of waste. (In addition, the Bangalore Corporation has 13 dumper placers for transporting metallic containers of 2.5 to 3 tonnes capacity and 6 mini-compactors for transportation of waste.)

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