ADVANCED SOLID WASTE MANAGEMENT (UNIT II QUESTION)

 

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PLEASE READ THE DIRECTIONS CAREFULLY!!!UNIT II QUESTION CAN BE FOUND IN THE SYLLABUS. THE WORK MUST BE COMPLETED IN THE TEMPLATE PROVIDED IN THE SYLLABUS. THIS CONSIST OF MATH AND WRITING. I HAVE PROVIDED AN EXAMPLE OF THE MATH AND THE SYLLABUS WITH QUESTIONS AND TEMPLATE. THE TABLE 3-1 FOR MANY OF THE QUESTIONS. PLEASE READ THE DIRECTIONS. DO NOT PLACE A BOOK IF YOU CANNOT COMPLETE THIS ASSIGNMENT CORRECTLY. 

TEXTBOOK CHAPTER IS INCLUDED

 Worrell, W. A., Vesilind, P. A., & Ludwig, C. (2017). Solid waste engineering: A global perspective (3rd ed.). Boston, MA: Cengage Learning. 

  • Course Syllabus
  • Course Description

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    A study of the growing and increasingly intricate problems of controlling and processing the refuse created by urban society.
    Includes discussion of issues concerning regulations and legislation with major emphasis on solid waste engineering
    principles.

    Course Textbook(s)

    Worrell, W. A., Vesilind, P. A., & Ludwig, C. (2017). Solid waste engineering: A global perspective (3rd ed.). Boston, MA:
    Cengage Learning.

    Course Learning Outcomes

    Upon completion of this course, students should be able to:

    1. Assess the fundamental science and engineering principles of solid waste management.
    2. Evaluate the evolution of technologies related to solid waste management.
    3. Assess the political environment as it relates to solid waste and solid waste management.
    4. Summarize laws and standards related to solid waste management.
    5. Describe best practices of solid waste management in an urban society.
    6. Relate leadership and management principles to effective solid waste management.
    7. Examine the impact of solid waste on human populations.
    8. Solve solid waste related problems through collaborative methods of problem solving.

    Credits

    Upon completion of this course, the students will earn 3 hours of college credit.

    Course Structure

    1. Study Guide: Course units contain a Study Guide that provide students with the learning outcomes, unit lesson,
    required reading assignments, and supplemental resources.

    2. Learning Outcomes: Each unit contains Learning Outcomes that specify the measurable skills and knowledge
    students should gain upon completion of the unit.

    3. Unit Lesson: Unit Lessons, which are located in the Study Guide, discuss lesson material.
    4. Reading Assignments: Units contain Reading Assignments from one or more chapters from the textbook and/or

    outside resources.
    5. Suggested Reading: Suggested Readings are listed within the Study Guide. Students are encouraged to read the

    resources listed if the opportunity arises, but they will not be tested on their knowledge of the Suggested Readings.
    6. Learning Activities (Non-Graded): Non-Graded Learning Activities are provided to aid students in their course of

    study.
    7. Discussion Boards: Discussion Boards are part of all CSU Term courses. More information and specifications can

    be found in the Student Resources link listed in the Course Menu bar.
    8. Unit Assignments: Students are required to submit for grading Unit Assignments. Specific information and

    instructions regarding these assignments are provided below. Grading rubrics are included with each assignment.
    Specific information about accessing these rubrics is provided below.

    9. Ask the Professor: This communication forum provides you with an opportunity to ask your professor general or
    course content related questions.

    10. Student Break Room: This communication forum allows for casual conversation with your classmates.

    MEE 5901, Advanced Solid
    Waste Management

  • MEE 5901, Advanced Solid Waste Management
  • 1

    CSU Online Library

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    e-books, and research guides. These resources are always accessible and can be reached through the library webpage.
    To access the library, log into the myCSU Student Portal, and click on “CSU Online Library.” You can also access the CSU
    Online Library from the “My Library” button on the course menu for each course in Blackboard.

    The CSU Online Library offers several reference services. E-mail (library@columbiasouthern.edu) and telephone
    (1.877.268.8046) assistance is available Monday – Thursday from 8 am to 5 pm and Friday from 8 am to 3 pm. The library’s
    chat reference service, Ask a Librarian, is available 24/7; look for the chat box on the online library page.

    Librarians can help you develop your research plan or assist you in finding relevant, appropriate, and timely information.
    Reference requests can include customized keyword search strategies, links to articles, database help, and other services.

    Unit Assignments

    Unit I Assignment

    For this Assignment, you will complete the Unit I Assignment worksheet. This Assignment will allow you to demonstrate
    what you have learned in this unit.

    Click here to access the template for this Assignment. Save all of your work directly to the template, and submit it in
    Blackboard for grading.

    To assist you with the math required in this assignment, the CSU Math Center has created an example problem using the
    necessary formulas. Click here to access this example.

    Information about accessing the grading rubric for this assignment is provided below.

    Unit II Assignment

    For this Assignment, you will complete the Unit II Assignment worksheet. This Assignment will allow you to demonstrate
    what you have learned in this unit.

    Click here to access the template for this Assignment. Save all of your work directly to the template, and submit it in
    Blackboard for grading.
    To assist you with the math required in this assignment, the CSU Math Center has created an example problem using the
    necessary formulas. Click here to access this example.
    Information about accessing the grading rubric for this assignment is provided below.

    Unit III Assignment

    For this Assignment, you will complete the Unit III Assignment worksheet. This Assignment will allow you to demonstrate
    what you have learned in this unit.

    Click here to access the template for this Assignment. Save all of your work directly to the template, and submit it in
    Blackboard for grading.

    To assist you with the math required in this Assignment, the CSU Math Center has created example problems using the
    necessary formulas.

    Click here to access the example for question 1. This example contains a recorded lesson with audio. Click here for a
    transcript of this lesson.

    Click here to access the example for question 2. This example contains a recorded lesson with audio. Click here for a
    transcript of this lesson.

    Click here to access the example for question 3. This example contains a recorded lesson with audio. Click here for a
    transcript of this lesson.

    Information about accessing the grading rubric for this assignment is provided below.

    Unit IV Assignment

    For this Assignment, you will complete the Unit IV Assignment worksheet. This Assignment will allow you to demonstrate
    what you have learned in this unit.

    Click here to access the template for this Assignment. Save all of your work directly to the template, and submit it in
    Blackboard for grading.
    To assist you with the math required in this Assignment, the CSU Math Center has created example problems using the
    necessary formulas.

    MEE 5901, Advanced Solid Waste Management 2

    mailto:library@columbiasouthern.edu

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitI_Assignment x

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitI_FrontLoaderGarbageTruckandDumpsterExample

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitII_Assignment x

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitII_MunicipalGovernmentandTransferStationExample

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIII_Assignment x

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIII_CoarserParticleSizeDistributionExample

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIII_CoarserParticleSizeDistributionExampleTranscript

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIII_HigherBulkDensityRefuseExample

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIII_HigherBulkDensityRefuseExampleTranscript

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIII_SellingLandfillCapacityExample

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIII_SellingLandfillCapacityExampleTranscript

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIV_Assignment x

    Click here to access the example for question 2. This example contains a recorded lesson with audio. Click here for a
    transcript of this lesson.
    Click here to access the example for question 3. This example contains a recorded lesson with audio. Click here for a
    transcript of this lesson.
    Information about accessing the grading rubric for this assignment is provided below.

    Unit V Assignment

    For this Assignment, you will complete the Unit V Assignment worksheet. This Assignment will allow you to demonstrate
    what you have learned in this unit.

    Click here to access the template for this Assignment. Save all of your work directly to the template, and submit it in
    Blackboard for grading.

    To assist you with the math required in this Assignment, the CSU Math Center has created an example problem using the
    necessary formulas.

    Click here to access the example for question 2. This example contains a recorded lesson with audio. Click here for a
    transcript of this lesson.
    Information about accessing the grading rubric for this assignment is provided below.

    Unit VI Scholarly Activity

    A local municipality expects to close its landfill in one year, and it has decided to adopt a thermal technology for the
    treatment of its municipal solid waste. The city needs your help to choose between a traditional municipal waste incinerator
    and a pyrolysis unit. As a solid waste professional, you have been hired by the city council to provide an analysis of these
    two technologies.

    You are tasked with preparing an executive summary that compares the two technologies. Your summary should contain
    the following items:

    a short description of the technologies, their advantages and disadvantages, their waste products, and their economics;
    the fundamental science and engineering principles of solid waste management that are involved;
    the laws or standards that factor into your decision;
    how your decision will affect the population of the community; and
    your recommendation and rationale to the city.

    Your executive summary should be a minimum of three pages in length. You must use your textbook and at least one
    resource from the CSU Online Library in your paper, but other academic sources may be used in addition. Any outside
    information used must be cited in accordance to APA style, and your paper should be formatted in APA style to include a
    title page, running head, and reference page.

    Information about accessing the grading rubric for this assignment is provided below.

    Unit VII Assignment

    For this Assignment, you will complete the Unit VII Assignment worksheet. This Assignment will allow you to demonstrate
    what you have learned in this unit.

    Click here to access the template for this Assignment. Save all of your work directly to the template, and submit it in
    Blackboard for grading.

    To assist you with the math required in this Assignment, the CSU Math Center has created an example problem using the
    necessary formulas. Click here to access this example.

    Information about accessing the grading rubric for this assignment is provided below.

    Unit VIII Scholarly Activity

    You are an engineer in a design, build, and operate construction firm. The firm has received four requests for proposals
    (RFPs) and can only respond to one of these. You have been asked to review the RFP from Washentaw County, Michigan,
    and write up a three-page executive summary for the marketing team. After reading all of the executive summaries, the
    marketing team will make a decision about which, if any, of the RFPs to respond to.

    The RFP from Washentaw County is located here:
    http://www.ewashtenaw.org/government/departments/finance/purchasing/online_bids/bid-status-previous-years/previous-
    year-assets/assets_2010/rfp6518

    Your executive summary should include the following items:

    an introduction that includes a detailed overview of the project scope;
    identification of the required information to be included into the company response to the RFP;
    your concerns about any of the obligations in the RFP;
    how any negotiations with Washentaw County could affect the decision (i.e.,What collaborative methods of problem

    MEE 5901, Advanced Solid Waste Management 3

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIV_SeparatingPlasticfromShreddedWastesExample

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIV_SeparatingPlasticfromShreddedWastesTranscript

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIV_MunicipalityBudgetforRecyclingProgramExample

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitIV_MunicipalityBudgetforRecyclingProgExampleTranscript

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitV_Assignment x

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitV_NaturalGasGenerationataLandfillExample

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitV_NaturalGasGenerationAtALandfillTranscript

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitVII_Assignment x

    https://online.columbiasouthern.edu/CSU_Content/Courses/Emergency_Services/MEE/MEE5901/16E/UnitVII_MethaneProductioninBTUperYear

    http://www.ewashtenaw.org/government/departments/finance/purchasing/online_bids/bid-status-previous-years/previous-year-assets/assets_2010/rfp6518

    solving could be used to solve the marketing team’s problem of choosing an RPF? How could these methods be applied
    to this situation?); and
    your justified recommendation to respond or to pass on this business opportunity. This should include a description of
    the leadership and management principles that factored into your decision.

    Also, as stated in the RFP, the criteria for making a decision will depend on the following three areas: price, collection and
    methodology, and responsiveness to the bid. While you cannot address the price issue, you can cover in your
    recommendation discussion the collection methodology and the level of detail that you would recommend when responding
    to the bid.

    Your response should be at least three pages in length. At a minimum, you should use information from your textbook to
    support your answer, but other academic resources may be used as well. Any resources used should by cited in
    accordance with APA guidelines. Format your response in APA style to include a title page, running head, and reference
    page.

    Information about accessing the grading rubric for this assignment is provided below.

    APA Guidelines

    The application of the APA writing style shall be practical, functional, and appropriate to each academic level, with the
    primary purpose being the documentation (citation) of sources. CSU requires that students use APA style for certain papers
    and projects. Students should always carefully read and follow assignment directions and review the associated grading
    rubric when available. Students can find CSU’s Citation Guide by clicking here. This document includes examples and
    sample papers and provides information on how to contact the CSU Success Center.

    Grading Rubrics

    This course utilizes analytic grading rubrics as tools for your professor in assigning grades for all learning activities. Each
    rubric serves as a guide that communicates the expectations of the learning activity and describes the criteria for each level
    of achievement. In addition, a rubric is a reference tool that lists evaluation criteria and can help you organize your efforts to
    meet the requirements of that learning activity. It is imperative for you to familiarize yourself with these rubrics because
    these are the primary tools your professor uses for assessing learning activities.

    Rubric categories include: (1) Discussion Board, (2) Assessment (Written Response), and (3) Assignment. However, it is
    possible that not all of the listed rubric types will be used in a single course (e.g., some courses may not have
    Assessments).

    The Discussion Board rubric can be found within Unit I’s Discussion Board submission instructions.

    The Assessment (Written Response) rubric can be found embedded in a link within the directions for each Unit
    Assessment. However, these rubrics will only be used when written-response questions appear within the Assessment.

    Each Assignment type (e.g., article critique, case study, research paper) will have its own rubric. The Assignment rubrics
    are built into Blackboard, allowing students to review them prior to beginning the Assignment and again once the
    Assignment has been scored. This rubric can be accessed via the Assignment link located within the unit where it is to be
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    Again, it is vitally important for you to become familiar with these rubrics because their application to your
    Discussion Boards, Assessments, and Assignments is the method by which your instructor assigns all grades.

    Communication Forums

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    Participation in these discussion forums is encouraged, but not required. You can access these forums with the buttons in
    the Course Menu.

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    Ask the Professor

    This communication forum provides you with an opportunity to ask your professor general or course content questions.
    Questions may focus on Blackboard locations of online course components, textbook or course content elaboration,
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    Questions that are specific in nature, such as inquiries regarding assessment/assignment grades or personal
    accommodation requests, are NOT to be posted on this forum. If you have questions, comments, or concerns of a non-
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    professor within 48 hours.

    Before posting, please ensure that you have read all relevant course documentation, including the syllabus,
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    MEE 5901, Advanced Solid Waste Management 4

    http://www.columbiasouthern.edu/downloads/pdf/success/citation-guide

    https://online.columbiasouthern.edu/CSU_Content/common_files/instructions/DB/Create_New_Thread_Subscribe

    Student Break Room

    This communication forum allows for casual conversation with your classmates. Communication on this forum should
    always maintain a standard of appropriateness and respect for your fellow classmates. This forum should NOT be used to
    share assessment answers.

    Schedule/Grading

    The following pages contain a printable Course Schedule to assist you through this course. By following this schedule, you
    will be assured that you will complete the course within the time allotted.

    Unit I Integrated Solid Waste Management [ Weight: 12% ]

    Read/View: Unit I Study Guide
    Chapter 1: Integrated Solid Waste Management
    Chapter 2: Municipal Solid Waste Characteristics and Quantities

    Discuss: Unit I Discussion Board 2%

    Submit: Unit I Assignment 10%

    Unit II Collecting and Handling Municipal Solid Waste [ Weight: 12% ]

    Read/View: Unit II Study Guide
    Chapter 3: Collection

    Discuss: Unit II Discussion Board 2%

    Submit: Unit II Assignment 10%

    Unit III Unit Operations for Processing Municipal Solid Waste [ Weight: 12% ]

    Read/View: Unit III Study Guide
    Chapter 4: Mechanical Processes

    Discuss: Unit III Discussion Board 2%

    Submit: Unit III Assignment 10%

    Unit IV Unit Operations for Separating Municipal Solid Waste [ Weight: 12% ]

    Read/View: Unit IV Study Guide
    Chapter 5: Separation Processes

    Discuss: Unit IV Discussion Board 2%

    Submit: Unit IV Assignment 10%

    Unit V Role of Biological Processes in Stabilizing Municipal Solid Waste [ Weight: 12% ]

    Read/View: Unit V Study Guide
    Chapter 6: Biological Processes

    Discuss: Unit V Discussion Board 2%

    Submit: Unit V Assignment 10%

    MEE 5901, Advanced Solid Waste Management 5

    Unit VI Role of Thermal Processes in Solid Waste Management [ Weight: 14% ]

    Read/View: Unit VI Study Guide
    Chapter 7: Thermal Processes

    Discuss: Unit VI Discussion Board 2%

    Submit: Unit VI Scholarly Activity 12%

    Unit VII Structure and Design of Municipal Solid Waste Landfills [ Weight: 12% ]

    Read/View: Unit VII Study Guide
    Chapter 8: Landfills

    Discuss: Unit VII Discussion Board 2%

    Submit: Unit VII Assignment 10%

    Unit VIII Integrated Resource Management [ Weight: 14% ]

    Read/View: Unit VIII Study Guide
    Chapter 9: Toward Integrated Resources Management – Environmental, Political, and
    Economic Issues

    Discuss: Unit VIII Discussion Board 2%

    Submit: Unit VIII Scholarly Activity 12%

    MEE 5901, Advanced Solid Waste Management 6

      MEE 5901, Advanced Solid Waste Management
      Course Syllabus
      Course Description
      Course Textbook(s)
      Course Learning Outcomes
      Credits
      Course Structure
      CSU Online Library
      Unit Assignments
      Unit I Assignment
      Unit II Assignment
      Unit III Assignment
      Unit IV Assignment
      Unit V Assignment
      Unit VI Scholarly Activity
      Unit VII Assignment
      Unit VIII Scholarly Activity
      APA Guidelines
      Grading Rubrics
      Communication Forums
      Schedule/Grading

    Collection
    Solid waste collection is an exercise in reducing entropy. The pieces that lllil

    ~

    up the solid waste are scattered far and wide, and-the role of the colk« II

    I

    I

    is to gather this material’together into one container. In .most parts I li

    t

    developed world, solid waste collection systems are invariably person/ru II 1

    systems. With only a few minor exceptions, the collection of MSW is don« I,V

    men and women who traverse a town in trucks and then ride with the II III I

    to a site at which the truck is emptied. This may be an intermediate stopover

    where the refuse is transferred from the small truck into trailers, larger v.m I

    barges, or railway cars for long-distance transport or the final site, such a lilt

    landfill, waste to energy plant, compost site, or materials recovery facility.

    3-1 REFUSE COLLECTION SYSTEMS

    !~e proc~ss of refuse collection should be thought of as a multiphase process, aII( I
    It ispossible to define at least five separate phases, as shown in Figure 3-1. HISI,
    the m?IVldu~1homeowner must transfer whatever is considered waste (defined .1

    /(

    ~a~enal haVl~gno further value to the occupant) to the refuse can, which may Ill’
    inside or outside the home. The second phase is the movement of the refuse Clil
    or bin to the collection truck, which is usually done by the collection crew and i.
    called backyard collection. If the can is moved to the street by the waste generato I
    or the home occupant, the system is called curbside collection.

    More.and mor~ separated materials (commonly called recyclables) and yar d
    wastes, which sometimes include food waste, are collected separately, either in sep
    arate compartments of the same trucks as the mixed refuse or in separate vehicles.
    The ~ollo~ng ~nalysis applies to any or all of these materials, although most 01
    the dISCUSSIOnISabout mixed (nonseparated) waste.

    ‘Iru ‘1

    Q Disposalor, transfern ,, , ,I I ,, , ,, , ,,,
    CD , 8)

    ,
    0), CD , ,I I I~I-c •• • -,- •• 1•• ——-I !rIll I’ I Can Truck from house I Truck I TruckI, I routing III’ I to to I I to

    III I truck house I I disposalI II , ,
    I

    ivephases of municipalsolid waste collection.

    III ‘ truck must collect the refuse from many homes in the most efficient way
    Ihl,’, and when it is full (or at the end of the day), it must travel to the mal ri

    /II IIV ‘Iy facility, the point of disposal, or the transfer site. The fifth phase of the
    IIr II Ill! system involves the location of the final destination (materials recovery

    II/y, lisposal site, or transfer station). This is a planning problem, often involv-
    IIIIH ‘ than one community.

    Phase 1: House to Can
    II II!lUS -to-can phase has received almost no attention or concern by researchers

    IIV -rnment because the efficienciesand convenience’sgained here are personal
    11.1 IlIll ommunal. Asdiscussed later under source separation, one major drawback
    ’11I11t’ ting separated material is the inconvenience suffered by the individual.

    Some communities use tax funds to operate the solid waste collection and
    Ii 1″111.1 system, or they charge for the service just as they charge for water con-
    IlIIqHi n and wastewater disposal. Such a system gives the generators of waste
    1/ III iii mche to generate as much as they please because the cost is the same regard

    ” or how much they contribute. The need to manage and control the amount
    ” ~llstegenerated has led communities to try novel ways of funding solid waste
    1’lIll\l(lms.Some communities have adopted a volume-based fee system to pay ()I’
    u] d waste collection and specify the containers that must be used. In a volume

    “, I’ I feesystem, residents are offered cans in three sizes-such as 19-, 30-, 60-, (JI’
    III f\1111on(72-, 110-, 230-, and 340-liter) cans. The fee for refuse service is based
    “” Ihe size of can used. Over 4000 communities have adopted volume-based
    1 II IS for solid waste collection. The EPAreports typical reduction of 25% to 3~)’Y.1
    !r II ommunities that have gone to volume-based rates.’ Other communiti ‘S OII’l’

    I,d 1111III “PI’IOIII” I II’ 11’1Iuuh ‘) II WI’ till “l ‘WI (.III III I Illllif “l II 1111III
    W ‘1\111;II • Is 1;,11′ 1111’ 1I1l’1.1{/II·tIllS(‘t/ jll(‘ .”‘.~II’III.

    Vt IUII\l’ I ase I /’ syst ms an ‘ilb’l’ I ‘ I()O%) varlnblc 1′,11′ 01′ Ii’ III I
    I 0%. F r .xnn I I ,II’ ( mrnunity r I’S 0·, 0·, r t O·g, II n w, Ill’ WIWI’II’I III
    garbag s rvi , th m m mity must I i I h w I I ri II S rvl ‘to 1′;1IH’ III
    ficient r V nu . In a 100% variable rate community, th O-gall 11w, ste Willi I I
    would be twice as expensive as the 30-gaBon wast wh el r. whil the I)() 11,1111111
    waste wheeler would be three times as expensive as the 30-gallon waste wll.,. II I
    Thus 30-gallon service might cost $12 per month, 60-gallon service wOlIlII • II I
    $24 per month, and 90-gallon service would cost $36 per month. Th IOO’YiIv,111
    able pricing encourages the public to maximize waste reduction. However, 1111’• II~I
    to provide the service is not 100% variable. Thus with the exception of the 1.111111111
    fee, it may cost as much to collect a 30-gallon waste wheeler as a 90-gall n W,IIIII
    wheeler.

    Some communities try to more closely tie the cost of service to the g,lI h.It,1
    fee. In the above examples, instead of charging $12/$24/$36, another Coml11\11I1I\
    might charge $20/$24/$28. While these rates might more closely match the 11I1I
    to provide the service, the cost difference between the different size waste whcrh I
    is smaller and thus there is not as large a financial incentive to reduce the amount
    of waste being generated.

    One study looked at 8 similar communities with the same type of service (11.1\’
    for garbage based on the size of the container and no additional charge for recyc 111’I
    and green-waste service”). Four communities had 100% variable rates and 11 h,1I1
    rates that varied by 23 to 88%. The communities with the 100% variable rates had ,III
    average garbage service level of 41 gallons. The communities with the less than 1 O( )1111
    variable rates had a garbage service level’ of 51 gallons.

    Pay-as-you-throw may have generated renewed interest in the home COlli
    pactor. This device, originally introduced in the 1950s without much success,
    sits under the kitchen counter and compresses about 20 lb (9 kg) of refuse into .1
    convenient block within a special bag. The bulk density of the compacted refuse
    is about 1400 lb/yd” (830 kg/m3), which yields a compaction ratio of about 1:5.

    A family of four people generates solid waste at a rate of 2 lb/cap/
    day, and the bulk density of refuse in a typical garbage can is about
    200 lb/yd” If collection is once a week, how many 30-gallon garbage
    cans will the family need, or alternately, how many compacted 20-lb
    blocks would the family produce if it had a home compactor? How
    many cans would the family need in that case?

    2 Ib/cap/day X 4 persons X 7 days/week = 56 Ib refuse
    56 Ib/200 lb/yd? = 0.28 yd3
    0.28 yd3 X 202 qal/yd? = 57 gal

    60-9 lion c n.
    i compacted into 20-lb blocks, th family would
    thr e such compacted blocks to take care of th

    . If ach block of compacted refuse is 1400 lb/yd”, the
    lume is

    II

    1111IlInlly would need only one 30-gal can.

    hase 2: Can to Truck
    II IIIIll’, II . most common system of getting the solid waste into the truck was
    11111’1101″oing to the backyard, emptying the garbage cans into large tote con-

    ” I I III’ I trying these to the w.~iting truck. This system was not only expensive
    I tll.lI st to the community, but it was expensive in terms of the extremely

    It III III rate to the collectors. At one time, solid waste collectors had the high Sl
    I 1111′ f any vocation-three times higher than the injury rate for coal min-
    fill ‘ , mple. Even now, with all ofthe improvements in collection technology,

    I I I I ollection is still one of the most hazardous jobs in America. A survey
    Iii II.S. Department of Labor’s Occupational Safety and Health Administration

    I II ) Statistics Department found that fully 40% of solid waste workers had
    I Ii time during the preceding year due to various injuries, including strains,

    I II I ,tlnd fractures.’
    l’h traditional trucks used for residential and commercial refuse col-

    1111111re rear-loaded and covered compactors called packers and vary in
    I I 1111I design, with 16- and 20-yd3 (12- and 15-m3) loads being common
    1 III’ -2). The truck size is often limited not by its ability to store refuse but

    1 wheel weight. Residential streets are not designed to carry large wheel
    ul I and refuse trucks can easily exceed these limits. Commonly, the refuse
    111’1t i d from garbage cans into the back of the packers, where it is scooped

    III I) hydraulically operated compaction mechanisms that compress the refuse
    1111111::1loose density of about 100 to 200 lb/yd” (60 to 120 kg/rn”) to about
    , 111110 700 lb/yd” (360 to 420 kg/rn”). The compaction (packing) mechanism

    I 1111’manufacturer is shown in Figure 3-3. In addition, many companies are
    IIIIVbuying natural gas fired vehicles (Figure 3-4). In combination with biogas

    IIIIHI~Ition from green and kitchen waste or landfills, these trucks could run
    tll I I gas from waste.

    Two revolutionary changes are occurring that have had a great impact on
    IlIlh the cost of collection as well as the injury rate of the collectors. The first is

    hi’ acceptance of the can-on-wheels idea, known as waste wheelers. These con-
    11111(,1’are provided to the customer by either the garbage company or the local
    municipality. The resident fills the large plastic container on wheels and then
    IIII h s it to the curb for collection. These containers can be used for mixed refuse,

    Figure 3-2 A rear-loading packer truck for collecting residential solid waste.
    (Courtesy William A. Worrell)

    !!-3 Compacting mechanism for a packer truck.

    recyclables, and/or yard waste (Figure 3-5). The collection vehicles are equipped
    with hydraulic lifters that are used to empty the contents into the truck as shown
    in Figure 3-6. The collectors do not come into contact with the refuse, thus avoid
    ing dangerous materials that can cut or bruise. In addition, the collectors do not
    lift the heavy container, thus avoiding back injuries. This system, referred to as

    (“,’funcill9pr01idedbythe
    s.ttlis~Airi’ltlIutitnCootro/District

    ~

    I 3 4 Natural gas powered packer truck. (Courtesy William A. Worrell)

    – – -.”,/ ‘~i~ ,.~·i,”‘” -‘1″‘:”~’ ,(I,~ n::””’ ~~ “‘1~ : ~

    t.
    ~. ” ~..__ ~t ;:L:.;t~~’.c.”,:..i!..-…L~ ,,’:”‘_ ~: L1 J ~~ ..::_ _ _

    Igure 3-5 Separate containers for recyclables, yard waste, and mixed refuse at the
    urb. (Courtesy William A. Worrell)

    Figure 3-6 Blue mixed recycling container being dumped into a truck.
    (CourtesyWilliam A. Worrell)

    semi-automated collection, typically requires a driver and one or more collector:
    A further development in solid waste collection technology is the can snatcher, .,
    truck equipped with long arms that reach out, grab a can, and lift it into the bark
    of the truck (Figure 3-7). Such systems, called fully automated collection, can 111′
    operated by a single driver. Communities that have converted from the manu.il
    system to the fully automated system have saved at least 50% in collection costs,
    much of it in reduced crew size and medical costs.’

    3-1-3 Phase 3: Truck from House to House
    Once the refuse is in the truck, it is compacted as the truck moves from house to
    house. The higher the compaction ratio, the more refuse the truck can carry before
    it has to make a trip to the landfill.

    Assume each household produces 56 Ib of refuse per week (as in
    Example 3-1). How many customers can a 20-yd3 truck that compacts
    the refuse to 500 lb/yd” collect before it has to make a trip to the
    landfill?

    yd3 X 00 lb/yd” = 10,000 Ib
    1 ,000 Ib/56 Ib/customer = 178 customers
    (Not th t the refuse weighs 5 tons, and if the truck itself w igh

    tons, the common 6-ton residential load limit can be exceed
    I fore the truck is full.)

    I 3-7 Automated garbage truck. Source:PeterCron/San LuisObispo C01111ly
    I I listed Waste Management Authority.

    ‘I’ll’ , 1’1(‘ )f Il\(‘ 11111 I I I ‘W ,\1\ 1,lIlf1′ 1101\1 Oil’ II OV ‘1’1 V’ I (‘upl’, II hilt I
    yard I i kUI Is )r~,1′ xl. fl larger I’ will>’.’ \ 11′ ‘d ‘ I I ‘(:llh • [II, I’ ‘w nilist Si’l II
    ans that might b at S m Ii tan rl’ III the )11′ Ii n v hi I’, ~lld skle pll IIIi’

    requires a smaller crew, and, of cours ,ru”y ut mal I YSl rns I’ tuirc 0111 1111
    person. Studies have shown that the great st v rail ffi i n i n b alt.1 III Ii
    with the smallest possible crews. For curbside refuse collection, thr -p rs n (11”1′
    do not collect three times as much refuse as a one-person crew.

    As a rough guideline, for most residential curbside collections, a si nglc 11111 I
    should be able to service between 700 and 1000 customers per day if th . I1IIII,
    does not have to travel to the landfill. In one California community, an autorn.uh
    collection system allows a truck to average about two and a half loads I (‘I d,l\
    (J Ovhour shift) at 10 tons per load.” Realistically, most trucks can service only ahl HI1
    200 to 300 customers before the truck is full and a trip to the landfill is nee SS,III’

    Suppose a crew of two people requires 2 minutes per stop, at which
    the crew can service four customers. If each customer generates 56 Ib
    of refuse per week, how many customers can crew members service
    if they did not have to go to the landfill?

    A working day is 8 hours, minus breaks and travel from and to the
    garage-say 6 productive hours, 6 X 60 = 360 minutes. At 2 minutes
    per stop, a truck should be able to make 180 stops and service 180 X
    4 = 720 customers.
    (Note, however, from Example 3-2, that the truck has to go to the
    landfill after only 178 customers or fewer still if its wheel loading is
    exceeded for the streets!)

    An organized way of estimating the amount of time the crew actually works
    in collecting refuse is to enumerate all of the various ways crew members spend
    time. The total time in a workday can be calculated as

    Y = a + c(b) + c(d) + e + f + g
    where

    Y = the total time in a workday
    a = time from the garage to the route, including the marshaling time or that

    time needed to get ready to get moving .
    b = actual time collecting a load of refuse
    c = number of loads collected during the working day
    d = time to drive the fully loaded truck to the disposal facility, deposit the

    refuse, and return to the collection route
    e = time to take the final (not always full) load to the disposal facility and

    return to the garage

    ull d,111 rcnl S In luding rim ‘It ‘010 the I il l
    nth ‘I’I )sl time su h S [I’ m jams, breakd wns, ‘l .

    II ill ,II I ‘S, 0 urse. hav t b in consistent time units, such a minut s.
    11111 \1\ nllt lysis, whil it may not be very useful for calculations, strikingly

    11111 lilill Ihfll ( working day is not the same as the time spent collecting soli I
    II III – ~’ III f b i.n the equation (the amount of time the crew a tually

    I 11111- ling I’ fus ) IS known, the number of customers served by that truck
    I II \ (.111 I ‘ stirnated.

    II II 1(‘,1 )11 is fairly homogeneous, travel times (d in the previous equation)
    I I I Innl d by driving representative routes and generalizing the data. One

    , I IIIIII,IV il-time data are available, the data can be regressed against the “crow-
    I lillH.. ne such regression” for New Jersey resulted in the expression

    1.<::'0 - 0.65

    II a tuaJ one-way travel time, min
    I ne-way travel time as the crow flies, assuming different truck speeds

    along the route, min

    1/ h crew can service 1.25 customers in one minute, what can crew
    mbers do in 4 X 60 minutes?
    1.25 X
    –=—

    1 4 X 60
    X = 300 customers per day

    If the number of customers that a single truck can service
    luring the day is known, the number of collection vehicles needed

    I r a community can be estimated by

    N = SF
    XW

    where
    N = number of collection vehicles needed
    S = total number of customers serviced
    F = collection frequency, number of collections per week
    X = number of customers a single truck can service per day
    W = number of workdays per week

    mmunity w ul n
    rs) th t are to be coil ct

    A single truck can service 300 customers in a single day and still hav
    time to take the full loads to the landfill.The town wants to collect on
    Mondays, Tuesdays, Thursdays, and Fridays, leaving Wednesdays for
    special projects and truck maintenance.

    SF 5000 X 1
    N = XW = 300 X 4 = 4.2 trucks

    The community will need five trucks.

    3-1-4 Phase 4: Truck Routing
    The routing of a vehicle within its assigned collection zone is often called mia 1/
    TOuting to distinguish it from the larger-scaleproblems (phase 5) of routing to IIII’
    disposal site and establishing the individual route boundaries. The latter problem
    is commonly known as macrorouting or districting and is discussed later.

    The present question is how to route a truck through a series of one- or two
    way streets so that the total distance traveled is minimized. Put another way, thr
    objective is to minimize deadheading, which is passing a collection point again
    after a previous pickup. The assumption is that if a route can be devised that ha:
    the least amount of deadheading possible, it is the most efficient collection route,

    The problem of designing a route to eliminate all deadheading was actu
    ally addressed as early as 1736. The brilliant mathematician Leonhard Eulci
    was asked to design a route for a parade across the seven bridges of Konigsberg,
    a city in eastern Prussia, such that the parade would not cross the same
    bridge twice but would end at the starting point. The problem is illustrated ill
    Figure 3-8 together with a schematic diagram. The routes are shown by lines
    called links, and the locations are known as nodes. The system shown has fall I
    nodes and seven links.

    Euler not only proved that the assignment was impossible, but he general
    ized the two conditions that must be fulfilled for any network to make it possible
    to traverse a route without traveling twice over any road. These two conditions are

    1. All points must be connected (one must be able to get from one place to
    another).

    2. The number of links to any node must be of an even number.

    The first condition is logical. The second similarly makes sense, in that if one trav-
    els to a location such as island A or B in Figure 3-8, one must be able to get off
    again-hence two roads. Euler’s parade problem had all the nodes with an odd

    I III 3-8 The bridges of Konigsberg.

    . . ible situation. The number of links connecting
    11111111or of links-sa clearly Impossth. f any odd degree nodes in a sys-. . d e and e existence a -III’ I deSIgnatesIts egree, d dh di I’Simpossible A system that has, th te without ea ea lllg . .
    hili ndlcates at a rou . al network and an Euler’s tour IS
    II I I ) I s of even degree is known as a untcours ,

    1111 I’ ti ally possible.
    6

    d d ends and other restrictions can often
    In the real world, one-way streets, ea. 1 ‘I is difficult One-way streets

    licati f the theoretica ana YSI .11111′ practical app icauon 0 b . ing again .that one must be able to
    IIII onsidered in Euler’s theory y recogmzl . Th ode with three one-

    1 ti s as one leaves It. us a n
    11\ I) a node ex~cty a~many I~e one-wa street leading away from it imrn ‘.
    ‘,IYIllreetsleading to It and a s.mgle I YthOUghthe number of links at that

    1111\ ·Iy makes a network nonUllicoursa , even
    ‘1111\ i even. . 1 aki g a system unicollrS:1I

    The development of a leas~-ckostFroutemvolveths;K6~gsberg bridge problemI 1 b of added lin s or examp e., I 1 the ea~tnum er ,. I (deadhead) links to make the system unicoursnl
    IIIlid require only t~o addltlOnath ‘I E Ids tour exists, and the problem isII lure 3-9), With this system, a eoretlCa u

    IIIIW ne of finding the proper route, f chi . the most efficient unicoursnl
    7 h .d d a means 0 a ievmgKwan as provi e c tho rocedure’ the Chinese post /111/11

    ( d I ided the name lor IS p .”I (work an a so provi k lly a series of loops where each no I’,I )b b .ng that networ s are rea””rJem yo servi . . . in the additional connecting links (deadhend~)
    ‘III ars exactly~nce, By ~mlml~ g e can in fact achieve an overall opu-
    11I1• sary to achieve a umcoursa sys~em,o~ k f the Konigsberg bridg’
    1IIIImsystem. For example, the umcoursa networ 0

    Figure 3-9 One possible route for the king’s parade.

    problem shown in Figure 3-9 is clearly a poor choice. (A new bridge is rcqui II d I)
    It would make much more sense to trade the two deadheads shown in Figlll t’ I I,
    for the two in Figure 3-10. The latter is an obviously more efficient solution, 1111
    skill of the route planner must come into play in such tradeoffs, since a sll(lIlll
    street with many traffic problems, in fact, may be a more expensive alternat iVI’ III
    a longer but clear street.

    Once a unicoursal network has been designed, it remains to route Ihe 111111
    through this network. The method of heuristic (commonsensical) routius; I”,
    found wide application.” The following set of rules apply to microrouiing. SIIIII
    of these are pure commonsensical judgment. and some are useful guid lilll”1 “II
    determining overall strategy when planning a network.

    1. Routes should not overlap, should be compact, and should no: III
    fragmented.

    2. The starting point should be as close to the truck garage as possibl ‘.
    3. Heavily traveled streets should be avoided during rush hours.
    4. One-way streets that cannot be traversed in one line should b 100111II

    from the upper end of the street.
    5. Dead-end streets should be collected when on the right side of th ‘ sIll’. I
    6. On hills, collection should proceed downhill so that the truck can (101’1

    FigurEo’ 3-10 An It rnativ route for the parade.

    (:I{ kwise turns around blocks should be used whenever possible.
    t\ Lon ,straight paths should be routed before looping clockwis .
    ” JI II’ rtain block patterns, standard paths, as shown in Figure 3-11, siloldd

    11’1i d.
    III II turns can be avoided by never leaving one two-way street as the Oil!

    I and exit to the node.I” (‘rules can be used to develop effective routes with minor deadheading.
    I I I is an example of some of these routing rules applied to a large ill'(‘,\,
    III r nmputer programs have been developed by a number of res arCil(‘IH,
    I III,Hll ,it has been found that the tours constructed manually arc allll(l, I

    1II’Il’I’ than those done by mechanical tour-building codes.’

    I \I !
    I 1\ i.’Il D D

    Start
    Finish D D

    tart
    Fini h e- ,—– ,—–,1

    D D D Di
    I D D D DI1I
    D D D D IIII

    I

    iD D D D
    I—— – – – – –

    11 Large loops usually result in efficient collection.

    Figure 3-12 A sample routing for a collection truck.

    3-1-5 Phase 5: Truck to Disposal
    For smaller isolated communities, the macrorouting problem reduces to one 0/
    finding the most direct road from the end of the route to the disposal site. FOI
    regional systems or large metropolitan areas, however, macrorouting in terms 01
    developing the optimum disposal and transport scheme can be used to great advan
    tage. The available techniques, called allocation models, are all based on the concept
    of minimizing an objective function subject to constraints, with linear program
    ming being the most common technique.

    The simplest allocation problem is the assignment of solid waste disposal 10
    more than one disposal site. Often the solution is obvious-the closest sources
    are allocated first, followed by the next closest, and so on. With more complex
    systems, however, it becomes necessary to use optimization techniques. The
    most appropriate one is the transportation algorithm, which is a type of linear
    programming. This technique is illustrated in Appendix 3-7.

    is aim l always collected with dumpsters, which ar I rg
    ” “I,ll II nt in I” that are commonly lifted overhead by a fron.t load

    ,111111111 I (Figur -1), Dumpsters range in size from 1.5 to 8 cubic yards,
    I IIII III(I, I mm n sizes being 3 or 4 cubic yards, As with the can snatchers,

    II I do’s n t hay to get out of the truck, which is both an advantag,e an I
    III, tllLlj,\’, In b th ases. the driver does not see what has been placed ill the

    t I III I. l lnz I’d us or dangerous materials can be transferred to the truck and
    1101 I III ‘ It ng rous situations in the landfill or combustor. At the landfill, the
    I I 1\ III- ull truck is then pushed out (Figure 3-14),

    1I'(t’nl innovation has been the development of the split container. In
    III I I’ mrnunities the dumpster is placed inside an enclosure. These

    ·13 A dumpster used for commercial collection.

    I Ire 3-14 Dumpster collection truck being emptied at a landfill.

    Figure 3-15 Split containerfor recyclables and garbage. (Courtesy William A. W “, “I)

    enclosures hide the dumpster from public view. Unfortunately the enclosuu-
    typically only have room for one dumpster. Thus it is difficult to add recycli111\
    service because there is no room for the recycling dumpster. The San Luis Obixpn
    County Integrated Waste Management Authority solved this problem by creati III’, ,\
    split dumpster. This dumpster has two separate locking compartments, which (,11\
    b.e se~iced by a standard front loader truck. When dumping garbage the recycling
    SIde IS locked, and when dumping recycling the garbage side is locked. SpC(i,Ii
    signs were developed to inform users about the split dumpster (Figure 3-15).

    Roll-off containers (Figure 3-16) are commonly used on construction si(rs,
    The roll-off containers typically range in size from 10 to 40 cubic yards. The 10-yd I

    Figure 3-16 Roll-off containers. Source: Peter Cron/San Luis Obispo County
    Integrated Waste Management Authority.

    II!) 1111 I. 111′(‘1I, l’d for d ‘J))oIILiOIl 111111 -rlal, whll ‘lh ‘1l0-ytl \ PO-iiI I) unlt: (‘1111
    t •• I I 111\’,11(I’, nsf r SL li ns ~ I’ hOUR h I I garbag . ‘l’h main rs ar II 111’1
    1111I11.IIII.Hlhn tak th full ontain rs to th lanlfills.Asp ialtrll”‘klrans-
    I III loll, rr onu in r c La tirn to the landfill.

    ANSFER STAllONS

    II II • wn ( lisposal unit is remote to the collection area, a transfer station
    “11II ‘d, 1\( a transfer station, waste is transferred from smaller colleen n

    I “Ii I I Inrg r transfer vehicles, such as a tractor and trailer, a barge, 0r a raiI-
    I, II

    11111\1″1’stations can be quite simple, or they can be complex facilities. The
    II I I tit . F, ility is based on its intended use, with small transfer stations typi-
    It I 11’14011a tipping floor where collection vehicles drop their loads. Wast ,
    I II I . IOe led into open-top trailers using a wheeled loader. More complex

    Ilf I IlilHi1L mploy pits for vehicles to dump into. Transfer vehicles then an
    II Iii II I y using a compacting unit. A facility also might have a tunnel for the
    I It I \'” I I to drive into. Chutes or an opening in the floor would allow thes

    III Ill’ I aded by having waste pushed over the edge into them. Some typi al
    I Ii I I \Iions are shown in Figure 3-17.

    luu fer vehicles can be as large as 105 cubic yards (80 cubic meters). The
    I I I If 111 f a transfer vehicle is limited by allowable wheel loads up to 80,000 lb

    1111111fI), In addition, many states also have weight limits on each axle. Some
    I II I i 111ns employ scales so that trailers can be loaded to their maximum
    IllId wet ht. The available payload is usually about 40,000 Ib (18,000 kg).
    II II 1V ‘hides are constructed from either steel or aluminum, which can affe I

    .1 III I payload.
    I \I of four methods is used to unload the transfer trailer:

    I. tlve bottom, or walking floors, on the floors of the vehicles. The back-an 1-
    [orth movement of the longitudinal floor sections causes the refuse to be
    I ushed out of the trailer.

    • Push blade, similar to the blade in a packer truck. A telescoping rod push’s
    11 blade from the front ofthe trailer, which forces the waste out. .

    I, I rag chains. Some vehicles have chains on sprockets that go from rhr
    r nt to the back of a trailer, and by pulling on the chain, the-refuse is

    d ragged out of the vehicle.
    I. ‘/’ipper. Some units have no unloading mechanism, and a large (iPI’I’1 Iii

    (h landfill lifts the entire transfer vehicle up at an angle, causing 1111’1111111
    10open and the refuse to slide out.

    II insfer stations can also transfer refuse to trains or even barges. III NI’~ Iill
    II111waste was transferred onto barges, which then moved the 1’\,(11,’1\’II. III
    l uudfill on Staten Island until the landfill closed in 2001. In St’,IItII. llil

    I. Iransferred to railroad shipping containers that are then pl.ll \’111111I I I
    It IIIlli] ment to eastern Oregon. Durham, North Carolina, sends .iI1111I II III
    I I 11ll.I.to southern Virginia. Los Angeles is also planning 10 , IiiI’ /11111.\

    (a)

    (b)

    (e)

    (d)

    Several typical transfer stations. (a)Dump to container. (b) Dump to trailer. (c)Store and
    -cktrailer. (d) Dump to compactor.

    11111101′ lundllll II Illlp ‘I’ Iii ;OUllly, C,IiIl()11l II. Oil :l murl: ,Illltlkl’ H(‘,lk,
    III II I “lid nr ‘liS IIL1h nil \11′ Ullin 01’\ nil’ I HI”‘ll Of’Sflll I 1’1-\ .ouuty hrln

    , ” \II Ililih cr S\, Ii I1S with 40-y II ( 0-111′) r II-off bins, whi h (I” then
    II” 1111′ 11.1 os: I sit,
    I” III 1)11 l build r n L LO buil I a transfer station is often an economi

    11111111 I’isi n. If th one-way haul distance from the point of the full-
    1111 ‘Ii I t th dis harge point is short, then it is likely that no transfer

    I I II” I’d. n th other hand, if the discharge point is far away and the
    11’11 v’hl 1 will have to be away from its primary role of collecting refuse

    It” 1\, lit -n c transfer station might be warranted. The relationship is illus-
    \I 1 f \11′ I ‘ – I 8. Where the two curves cross is the breakeven point. Longer

    II wa rra n t the construction of a transfer station, while shorter hauls
    I III \ 1111′ nornical.
    \11I It I I III if a transfer station is economical, the cost of direct haul must be

    II II \11 III ‘ st of a transfer station. Direct haul is a variable cost based on
    Illdl ‘1 t) mil s that have to be traveled. A transfer station also has a variable

    I II 1111 th transfer vehicle mileage but also has a fixed cost based on the
    III I npcr ling cost of the transfer station. The variable cost for direct haul

    I 1\ II I vchi Ie is typically expressed as a cost per mile. The fixed cost for a
    I I 1.11on is based on cost per ton.

    III •• unple, if it is 40 miles round trip to a landfill and it costs $1.50 per mile
    I .ul a truck carrying 5 tons of garbage, the cost would be $12 per ton. If a
    I II I’ [Lying20 tons of garbage cost $2 per mile and the fixed cost at the
    \.1\ Oil i $5 per ton, the cost would be $9 per ton. Thus, a transfer station

    1’1 11111′) onomical.

    Haul distance to disposal

    Breakeven point of transfer stations.

    SOIIl ‘(1111 •• ,I (I’lll, / -r 1,,11011 1111’ ‘(/ll I ‘li IPI.lldl’, 0/ dl,lollH ‘ ((J” LInd/II III
    minimize th unl’n an I, ir I lIuli I) 11111 fl 11I.Il.l 1,111 1111, ,I I l’I’l\lil ma Illllll III
    landfill to only riving wa l fl’ m trans ,.Sl,lli ns. ‘this si nif antly I’ ‘dwI’ 1/11
    number of vehicles travelling to a Iandf II.

    In situations where the sophistication of linear programmin m d ‘Is l. 11111
    warranted, a brute-force technique using a simple grid system an b (V:lI’I1′ III
    this case, the region is divided into equal blocks on an X-Y grid, and the ,11/ ”
    waste generation is then estimated based on population. The sites for 11’:111’01, I
    stations and final disposal facilities are initially screened to eliminate bvioll’liI
    inadequate areas [e.g.. urban areas for landfills). Trial-and-error siting of (;leiIIII,_
    is then used to obtain the most reasonable combination of solid waste displI~1I1
    facilities.

    3-4 COLLECTION OF RECYCLABLE MATERIALS

    Recycling entered the mainstream of solid waste management in the I C).)(}
    No longer was recycling conducted by underfunded, idealistic individuals, 11111
    rather, multinational garbage companies were now involved. Recycling, reg.url
    less of the price paid for recycled material, could be profitable. While some 10111
    for the days of the idealistic recycler, no one can dispute that more materi.il I
    being recycled today. In 2008, approximately one-third of the MSW being grlll’l
    ated is recycled.

    Two factors have caused recycling to succeed. First, government has provider]
    leadership in the area of waste reduction. Over 40 states have adopted waste red I/(
    tion goals, and some states have set mandatory goals, with noncompliance result
    ing in fines of up to $10,000 per day. Second, the public has accepted the conrcp]
    that recycling is not free. lust as residents pay for garbage service, they also IIOW
    pay for recycling. Over 8600 curbside recycling programs have been implemeJlI(‘(I,
    resulting in 86.2 million tons-or 34.5% of all solid waste-being recycled
    Table 3-1 highlights the progress of recycling in the United States.

    Some groups, such as the Grassroots Recycling Network, see this as only 1111′
    beginning and are calling for a zero waste goal.’ 1

    To waste, to destroy our natural resources, to skin and exhaust the
    land instead of using it so as to increase its usefulness, will result in
    undermining in the days of our children the very prosperity which we
    ought by right to hand down to them amplified and developed.

    -Theodore Roosevelt, Seventh Annual Message, December 3, 190’1

    Progressive communities, such as San Francisco, have adopted a zero wasu:
    goal. The California Integrated Waste Management Board has embraced the zcn I
    waste goal and uses the slogan, “Zero Waste-You Make It Happen.”

    A major barrier to the increasing expansion of recycling is finding markels
    for the material. Recycling cannot occur without markets for the recycled material,
    and markets are created by using post-consumer material in the manufacture 01
    a product.

    Recovered

    (millions of tons) (percent of generation)

    rbo rd 64,6
    27.7
    33.0
    19.8
    68.0
    8.8

    17.9
    15.7
    15.2
    28.3

    4.8
    57.7
    34.5

    44.4
    3,0
    5,6
    0.7
    1.4
    2.8
    1.4
    2.3
    2.4
    1.3
    1.7

    19.6
    86.6

    I’ll) lu rs are being urged to take responsibility for the products they produce
    II ‘II ‘ that the material is either recyclable or that it uses post-co.nsumer.recy-
    I IIhll ‘rial. For example, the soft drink industry sells its product~ III aluminum

    111,11 asily can be recycled, and these cans already contain a high per.centage
    I” YI I’d aluminum. On the other hand, the industry also sells products m.PEfE

    I I I I mtainers that are much more difficult to recycle a~d are rarely used m ~he
    “,1111 lure of new bottles (unlike in Europe and. Australia, where the soft drink
    III Ii uses plastic containers with recycled plastic). .

    II’ ause the recycling industry is still young, there has n~t b~en time to se~tle
    ” 01 NI, ndard system that has a high probability of succee?mg !n every applica-
    .u 1\11 h community has almost an infinite number of options m how to design
    III ling program. . .. . th

    Many communities have switched to havmg their citizens place all e
    , l.ible material into one container. A separate truck takes the recyclable to .a

    II iI,11 recovery facility (clean MRF) for processing. ~ecause. the recyclable~ ale
    It \ P rated by commodity but instead placed comm~ngled mt~ one contaI~er,

    II ailed commingled collection of recyclable ~atenals (~.eeFIgure 3-~9). Ihe
    III for processing commingled recyclable matenals (see FIgure 3-201) IS much

    uuller than a MRF that must process both recyclable and non-recyclable ~aste
    “/’l’ MRF). However, the tradeoff is that ano~her truck must travel the same route
    I I’ I up the garbage. In addition, the resI.dents. must separate the recyclable
    I til’lials and place them in a container for this option to work. .

    orne jurisdictions have used one truck to pick up both ~ohd waste and
    uuningled recyclables in a dual-compartment packer truck (~lgure 3-21). The

    1111 has two lifters and is fitted with dual compartments: one SIde for recyclable
    I ill’rials and one side for solid waste. The contents of the two compartments

    t

    Figure 3-19 Commingled recyclables on the receiving floor. (Courtesy William
    A. Worrell)

    Figure 3-20 Storage bays for the separated recyclables. (Courtesy William
    A. Worrell)

    (a)
    (b)

    HI 3·21 (a) Dual-compartment packer truck, one side for garbage and one side
    I If mrninqled recyclables. (b) Two tippers, one for the garbage side and one for

    I 1 r yclables side. (Courtesy William A. Worrell)

    1111I1 n split during the dumping process, and the mixed refuse then an ht:
    “”11>’ ted to achieve a full load. The advantage of this system is that nly OIl(‘
    11111 and driver is needed to collect both the solid waste and recyclable m:lI(‘1’1
    I II wever, the amount of material collected must be balanced so 111:11 h0111
    ‘111’1 f rtments fill at the same rate. If only one compartment is full and Ill(‘ 01111’1
    lilli, the system loses its advantage. Because the truck now has to disch,llg’ ,II
    II I cations, the landfill and MRFalso must be near each other to mni nt.i II IIII

    II Ii ncy of this option.

    1\110111’I’oprlou tor « 11’llilll ‘0111111111,1(‘dI ‘( (I.lhl’ 1″.lll’l ,II , 111(‘//1,11′ /,,1
    system in whi h the I’ Y I blcs r place I ill II sP’ ‘ial bill’ h.\ I iov] 1’1 to III 1,\
    each customer. The same rruck that pi ks up L1I’ S lid w

    One disadvantage of any system that collects commingled re y I bl ‘S i,’ 1111
    potential contamination of the paper products by residual liquids in the gl.,” ,
    aluminum, or plastic containers. In addition, the sorting costs for co111III illl’,l1d
    recyclables can be high. In the 1990s communities initiated collection prUgJ,lIll11
    where the residents separated the materials and placed them into two or IhIII
    containers. For example, bottles and cans go in one container, newspaper i” ,I
    second, and mixed paper in the third. This eliminates the need to sort newsp.uu-i,
    which is the most common recyclable (by weight) and shifts the cost of so 1111’1\
    to the waste generator. This system requires trucks with multiple comparuncuu
    (Figure 3-22). While this method has a low initial cost, the participation 1.111′
    may be low. In the past 10 years, as more MRFs were built, many corn mun
    ties switched to the single commingled waste wheeler for recyclables. When 111’1
    Angeles switched from this method to a commingled container, the recycling 1.111′
    increased by 40%.12

    Yard waste also typically is placed in a separate container. These yard W<1~tl' programs are being expanded to include food waste and in some cases paper ,11111 compostable bags and utensils. A third truck is needed to collect the yard W.l~II· and take this material to a mulching or composting operation.

    In addition to these items, some communities have implemented curbside
    used motor-oil collection. Residents are allowed to place their used motor oil .11
    the curb, where it is collected to be recycled into new oil. Other communities haw
    tried curbside collection of batteries, paint, and other products.

    Both experience and mathematical modeling suggest that collection of COlli
    mingled recyclables on a per-ton basis is more expensive than the collection (ll
    mixed refuse. As would be expected, the cost on a per-ton basis decreases with
    higher participation rate and conversion to a single stream automatic collection
    system. If the income from the sale of recycled materials is taken into aCCOUI11,
    however, the cost of collecting recycled items is not significantly different from till’
    cost of collecting mixed, unsorted refuse.

    A curbside recycling program can divert between 15% and 30% of tll,’
    residential waste and costs between $2 and $5 per month per customer, depend
    ing on various options. An organics program can divert between 15% and
    30% of the residential waste and also costs between $2 and $5 per month.
    One study concluded that the cost of a typical suburban recycling program
    is between $114 and $120 per ton of material collected, based on a 50’V<1 set-out rate. 13

    Everett et al. have developed a model that estimates the cost of collecting
    partially separated (commingled) recyclables at curbside.” The model estimates
    the time to collect such waste and to sort it at the truck into various individual
    components. Three variables in the model are travel time, sorting time, and wait
    ing time (at stop lights, for example).

    (b)

    .22 (a) Workers place different recyclables in separate. bins (b) Bins are
    I into separate compartments in the truck. (Courtesy William A. Worrell)

    I’I\Wl time is estimated as

    D
    ‘1’=—–

    L(I-e-1ID)C

    I’ \I d
    I’ “” travel time between two consecutive stops, secon s

    I = travel distance between two consecutive stops, m (ft)

    L I(

    ~rew Size (km m I)
    (m I)

    ~ne person 18.8
    2.2 X 10 7

    Two persons 24.3
    1.7 X 10 2

    30urce: Based on Resources, Conservation and Recycling 22, Everett, S. Maratha, R. D rah.i], .\11,1
    =>. Riley, “Curbside Collection of Recyclables I: Route Time Estimation Model,” Pages N . 1// I’)

    L = calculated coefficient, km h-I (mile h-1)
    k = calculated coefficient, rn” (tr ‘)
    C = conversion factor, 1.467 for American standard units, 0.278 for SI 1\11\1
    The factors Land k vary with crew size, the maximum speed attaine I hy 1111

    iiJehicle,the acceleration, driver ability, and road conditions. The values of L ,llltl/,’
    3S estimated by Everett et al., are shown in Table 3-2.

    The time to walk to the containers and bring them back to the truck ,III III
    estimated as

    W = O.86A
    iOVhere

    W = walk time, seconds
    A = average walk distance at a single stop, m

    The sorting time is estimated as

    S = 21.3 + 2AB
    =or a one-person crew, and

    S = 23.2 + 1.8B
    =or a two-person crew, where

    S = average sorting time of a single set-out, seconds
    B = average set-out amount, kg

    :)n average, the set-out amount for a typical curbside program varies between (U
    and 12 kg.

    Finally, the truck has to navigate the streets, and if the traffic is heavy andl
    :::>rif there are many stop signs and traffic lights, there could be considerable w.il:
    jme. This can be estimated as

    .vhere
    E = average wait time at traffic lights and stop signs, seconds

    Ms = mean time spent at stop signs, seconds
    Ns = number of stop signs
    ML = mean time spent at traffic lights, seconds
    NL = number of traffic lights

    III lllod’l (with these varial lcs) has be ’11 foun I I prcdi l rhc time (e. I’
    111111 wlrhln IO’l/o flh tual valu ,1’1

    1I1’1\l’V ‘I’ r urbsid pr gram is initiat d in a ornrnunity, th l ad r want
    11111 v how su ssful it has b en. Success can be measured in many ways,

    III hid III rh ‘8 :

    II Ii I IIII or r fus rnponents diverted from the landfill, tons/week
    II II I (Ill If h us holds participating in the program; participation can be defined
    II 1111111 ways, such as having set out recydables at least once a month
    II Ii I IIIl h useholds participating on any given week
    1’1\ II I (‘I’ rn the sale ofrecydables, $/week

    II III lit IS rn thods are useful, but they have to be well defined and used consistently.
    III th world of MSW, the holy grail is to be able to weigh how much refuse

    1111 Ililll’ hold or business generates. To determine how much refuse is generated,
    III \ l’I,h, of each container must be measured every time the container is ernp-

    t! II ,I h usehold has three containers, one for garbage, one for recyclables, and
    III 1m r n waste, then each container must have a unique identification number

    II 111111 r uency identification (RFID) chip) and the associated empty weight. This
    I II I lus has to be developed for all the containers in the city. When the truck
    tlljll •• the container, the truck must be able to record the container number and
    II ,II III I weight of the container. With the unique identification number and the

    , ill W -lght, it is now possible to determine how much refuse was collected.
    ‘1’11 difficulty is that trucks must be retrofitted with a scale, identification

    I III II ,'(RFID chip), reader, and recording device. After much difficulty one com-
    I uulry r trofitted identification numbers on containers, developed a data base, and
    ,hil’l the scale and other equipment on the truck. What was measured was mat
    I HI .n-waste container weighted on average 49.8 pounds, the garbage container
    I III unds, ~nd me recycling container 18.4 pounds. However, the set-out frequency

    1111 Iii) ontamers was the opposite of the weight, with recycling containers being
    •I IIIIl most frequently, followed by garbage and green waste the least frequently.

    111I,dly, the average generation by weight for the households was 43% garbage, 30%
    I .Inbles, and 27% green waste. While this was one of the first attempts to quantify

    ” .unount of refuse being generated on the household level, one must be cautious
    II • tr polating from the results because of the small sample size.

    LITTER AND STREET CLEANLINESS

    11111’1′ is a special type of MSW. It is distinct from other types of MSW in that it is
    ulid waste that is not deposited into proper receptacles. As one travels around

    till w rid, it is fascinating to see all the different receptacles developed for garbage,
    I I lables, or organic material (see Figure 3-23). Unfortunately, if the public do s
    IIII 1I e these receptacles, litter is generated.

    We usually think of litter as existing in public places, but litter ould b n
    I’rlv,Itepremises as welL Although litter is usually considered to b visual affro11 I
    IliI , it also may be a health hazard. Broken glass and f od (or rats HIT bill two

    ~ 3-23 A collage of public receptacles. (Courtesy William A. Worrell)

    examples. Litter is also a drain on our economic resources, because the public m IISI
    pay to have it collected and removed when it is on public property.

    The collection of litter is of secondary importance to a community, because
    it does not represent a critical public service as do police and fire protection, watci
    treatment, and collection of refuse from residences and commercial establish
    merits. Litter removal is expensive, costing municipalities in the United States and
    Europe billions annually.

    The composition of roadside litter can vary considerably from place to place,
    as can the method of data collection. One major problem with any litter dat.i

    I Ilhll 111’1”I ()IIS 1.111to sp’clly Ill’ !-\ulddil1 ‘S IIS(‘I in the 011′((i()n nnd
    111i111111l111’I’Hllds’ldctnsl ifylh way in whi h th I r ‘Illng’softh’

    111111iII1(’11ISw ‘I” (I ul l d. I,’ J ample, a br k n b III an b unrcd
    I 111111(’11\)I” 111

    ouru

    1I’lii I Y( tual count

    II 11\l’It k of a standard counting technique, the following guidelines for
    hi I “I 1111’I’ studies are suggested: IS

    I :1Hill I as one item all pieces larger than 2.5 cm (1 in.). This count indu lcs
    !I’II\ ivable tabs from beverage cans.

    , I)() n l count rocks, dirt, or animal droppings.
    :OIIlHas one item all pieces of any item clearly belonging together, su h

    II .1I roken bottle. Otherwise, count each piece of glass, newspaper, and
    () 011 ingly.

    1)0 11 t count small, readily decomposable material, such as apple cores.
    I 1101’r adside litter surveys, measure all items within the officially deslg-

    n.u d right of way.
    I Empty liquids out of all bottles and cans before collecting them.

    IIII’ lin r survey, if conducted along a road, should be started by driving
    III lit’ I’ d at a slow speed and having a passenger record the visible items into
    I” 1\'(order for future transcription. Next, the litter is identified, recorded, and
    1111111llected. The items should be separated during collection into as many

    I 11″111.nt as feasible. The collected items are then weighed and the volum
    I 1III’cLThe relationship between visible items and total items along a roadside
    II,’ vn in Figure 3-24. It is interesting that along fairly clean roads, the visible

    ” I 1111is only about 6% of the total litter count! These data also confirm that a
    , 1,,1lion of our visible litter is bottles and cans.

    Por ommunity litter surveys, the photometric technique developed for Keep
    \11I 1.\ Beautiful, Inc. (KAB) may be used.” The blockfaces of a community ar
    I I numbered. and a preliminary sample size is established. About 5% of the
    I I. I /.\ s are usually adequate. Using the random number technique, the block-

    •. und the locations on those blockfaces to be measured are selected. As shown
    I HilI’ 3-25, a marker is located in the front center of the survey area, and a

    II,III ard is used to identify the location and date. To facilitate the counting of
    1111 I II’ m the developed photographs, a picture is taken of a clean pavement laid
    III with white marking tape in a 1 ft grid, 6 ft wide X 16 ft long, which is parallel
    1.1 II’ et curb. A transparency ofthe grid is prepared, and the resulting 96-square
    lid Is placed on top of each litter photograph. The litter is then counted and
    I, fi d using a magnifying glass. The first photographs are used for establishing
    III ha eline litter conditions. The litter rating (L) is calculated for each pictur
    “lIlllion) as the squares containing some litter compared to the total number of

    1 00,————————–,0-,

    II) 500:::0.-

    –_/- – – – ..0~~–~._—L~~-i——L—~o 1000 2000 3000 4000
    Total litter (items/mile)

    5000

    Figure 3-24 Results of a litter survey on a rural road. Source: Vesilind, P.A. 1976.
    Measurement of Roadside Litter. Durham, N.C.: Duke Environmental Center,
    Duke University.

    Camera
    —–:;;..•T

    _———M;rker ,/”” 15ft,+——- Survey area 1#”” t
    I” 16ft .+-7.5 ft –l

    Side view

    Chalkboard

    6}1~1==========~§~~:~~~~
    “”1″~——16 ft —– .•.•f-7.5 ft :.J

    Top view

    Figure 3-25 Keep America Beautiful litter measurement technique. Source: The
    Photometric Index. n.d. Stamford, Conn.: Keep America Beautiful.

    6
    3
    1
    4
    1

    6
    6
    3

    16
    5

    36

    6
    12
    9

    64
    25

    116

    Il'” 1111.11 1.11’1\’1111′ plwloWlIpils H\ ‘ i1l1aly'” ‘U all I Ill’ I. , (ill< u· '\ ( I'sall1l ling Sll '$ nc .ssary (111be HI ulat -d "8

    ,H)8i

    N ample .iz n eel d to make a O.5-poi.ntdifference between two (tv .\
    II – lit; r ratings (L) in an area, significant at the 90% conf II . level
    v.u lan or the litter ratings (L) of the initial photographs

    ,I ulated as

    II., F(LY (,~ FLy
    /1 __ –

    n – 1 n(n – 1)

    I I Ii Ll r rating of the ith photograph
    1/ I tal number of photographs
    /1 [r quency, or the number of photographs with anyone L

    III pose that a to~n has 600 blackfaces .and that ~ 5% sampl~, or
    ( lockfaces, is photographed as explained previously. The litter

    I II n s (L) are as shown:
    Number of Photographs

    L F FL FU

    1
    2
    3
    4
    5

    Ilow many blackfaces need to be photographed for a litter survey?
    he SZ is calculated as

    2 = 116 _ (36)2 = 2.5
    S 30 – 1 30(29)

    If SZ = 2.5, the number of sampling sites necessary is

    N = 22.8 (2.5) = 57
    In other words, 57 – 30 = 27 more sites are needed in order to have
    a statistically satisfactory baseline.

    1,I11(,lllwOI:’Ih’,II! (“III h’wllIl’OIIl’1 h (IIH”I V’, ,()( ,II, lUl(l 11’111111111I
    111ans. A gnltlvc solutl I) would I OIlV nrlu I ‘Ol/(‘ 1101 II) 111(‘1;.1 II I
    solution would b d priving th publi f Items Ihfll mil hi IW(()IIH’ 1111I
    finingpeoplewholitterheavilyiftheyar aught: nd a i hnlcal : lutlun ‘11111
    be simply cleaning up after littering has occurred.

    The first option demands an explanation of why peopl liucr, II lIllI ilil
    requiring studies on the psychology of litterers. ln one study.” Ih :II I 1111 ,
    272 persons were observed when they bought a hot dog wrapp d in P’II” I I I
    interest was the final deposition of the wrapper. Ninety-one p pi’ (1IiI”
    dispose of the wrapper improperly (they littered). The probability or ,111\ III
    person littering, based on this sample, could be calculated as

    E = 0.019 + 0.414(A) + 0.1654(C) + 0.1532(D)
    where

    E is the probability that a person would litter
    A, C, and D = 0

    except that
    A = 1 if the person is 18 years old or younger
    C = 1 if there are no trash cans conveniently located
    D = 1 if the area is already dirty with litter

    From the study, it is clear that age is quite important-younger IWIII’/l
    being much more likely to litter than are older persons. There was no stat i~111.11
    difference between 19- to 26-year-olds and persons older than 26 years. Celli II,
    was found to be statistically insignificant. Because the study was conducted II
    1973, its validity to today’s urban populations may be questionable. Intuitivrlv
    however, the role of younger persons as the major contributors to urban lilill
    remains valid.

    person littering a dirty

    That is, of 100 people answering that description, 33 would probably
    litter the street.

    Such studies yield clues as to how persons might be induced not to litter
    (e.g., put out more trash cans and clean up the street) and who the target popula
    tion is (e.g., young people).

    111111II (11()lof y ,111(/ ” ,iI Ollt 111’1 l”Iv’ h ‘(‘II II ‘( 1(‘ I ,II I IId”If’ (lIll
    111111’tll’ Jl ‘op/(‘ 11)( 10 III “‘.111 011’, III ly.” movie th ‘HI ‘I’ PUll’OIISdurln]
    II 111111ill'” W ‘I” nsk ‘<1by S'V ral 111.ans 11 I I liu I' rh . III 'fll 'I'. 'I'll ' rotnl III III 111'1 was th 'I) JiI' SLlI' I I1d us d as 11indi c 1 I' r ih su 'IlS thut

    I ‘I’ll/Oil 11, ‘I’hc r ‘suits sh w d that m a ures su h as I r nal xh rtari n
    II I It Ii I1I1.uid arui-liu I’ artoons had no effect on litter, but that I ayrn nt
    “‘ \ 101 plc ‘S r llu I’ at the end of the showing resulted in about a 9~%

    Ihlll II Illl ‘I”.Th I ar indication is that self-interest, such as placing a sub-
    1,1 ” III I )11b v rage containers, is an effective force in convincing peoj I
    ,lilli,
    IIll I (III l rn th d of litter control is to prevent items that might become lit-

    1’1I’ ‘/I hi ng the consumer. In the earlier example of the hot dog wrapp 1’,
    ‘1’11Ir ‘< s nable to suggest that 100% litter-free results could be obtained 11114List rners a paper wrapper around their hot dog. The banning or

    I) I “LISIi bags is a practical means of controlling this type of litter.
    IIII thlr I m thod of litter control is to clean up the mess once it has occurred.

    11111[s mmonly used in sports stadiums and other public areas where no
    “I 11111[ ‘t ask people to properly dispose of their waste. For roadside litter,

    III 111,11th most economical litter control alternative is actually frequent
    I III’

    II ‘I~’ live means of litter control is to enlist the help of the community
    , III}\organizations “adopt” a section of roadway. Organizations as varie I

    11111111gr ups, Rotary Clubs, sports teams, and even private businesses have
    I III kc .p sections of roadways clean by conducting periodic litter pickups.

    1111II\ ) I f litter control not only keeps roadways and streets cleaner, but i1
    Iii 11K the litter problem down to a personal level. Anyone who has contrib-

    I I .itur lay to the hot and dirty job of collecting litter along the roadway will
    IIIIIIWIr

    urnipts also have been made to design mechanical litter collection
    111111′, ne towed device has proven both inexpensive and effective. It works

    II I Iii!’ series of rotating plastic teeth that fling the litter into a collection
    I. I (11lL!h like a leaf collector connected to a lawn mower). 19A more sophis-
    II II .md ambitious unit uses a vacuum arm on a truck to suck up the roadside
    I

    I n.illy, street cleanliness can be negatively affected by the very people who
    II I I III household refuse. In a study at the University of Florida, litter was
    I 1111d using the KAB method on typical residential streets before and after
    I, ‘I I llection.” An almost 300% increase in litter was noted. The collection
    I” I I or believed the reason was twofold. First, he believed that his automated
    II 111011vehicles were poorly designed and that they were not always able to

    I iything into the truck. The second reason was that the city had initiated :1
    1111111′.ased refuse collection charge. He suggested that the residents had been
    I. III II the “Seattle Stomp” -a tricky two-step that originated in Seattle when
    I I t switched to volume-based collection. Residents had figured they could

    ‘”1111 refuse into a can if they stomped on the refuse and packed it into th
    II l hl led to the garbage being stuck in the can and to the potential for spillage
    111111the transfer to the truck.

    3-6 FINAL HOU H S

    In “the good old days,” the garbag man arnc twi ‘a w “I, went lO OIl! It I
    yard, and collected all your garbage. Today, sorn mn uniti s have 1111\’1’dill
    ent-sized garbage cans, three recycling containers, a yard W:lSI ol1l:1iIWI,.11111
    used oil container. Collection may involve up to 3 fully automat d v .h iell’s, d II
    by a man or women who collects these materials using a joystick instead 01 I III
    a 70 pound can. The instructions on how to put your garbage out arc ,1111111I
    complicated as those for operating your cell phone. Yet, with all this ompk: \I
    is working. Why? Because many people have an environmental ethic and It’llllIlll
    the need for integrated waste management. In 2012, only 40% of the Unil(‘d ‘.111
    population voted, while at the same time 58% routinely recycled.

    The limits to recycling are still unknown. Learned people are debating will III II
    is possible to even think about recycling all of the materials we consider wasIl’ ~Ii
    likely, fundamental principles of physics” and thermodynamics” and mass 11.IIIhliI
    make the goal of 100% collection of materials impossible. It is quite likely Ih,ll, wll II
    the environmental effects of recycling are compared to the impact of disposal (1111ItIII
    there will be some point at which more recycling will actually have increasingly IIIIII
    mental effectson energy use and materials conservation. At the present time, II(IWI’II
    one of the major objectives in solid waste engineering is to effectively and eml Ii III
    collect all of the materials people no longer want. Because the collection of 111111111I11I
    solid waste accounts for between 50% and 75% of the total cost of refuse 111.111111′
    ment, it is important that solid waste engineers properly design collection SyS\(,111

    Finally, it is important to recognize that garbage collection is still a 1.111111
    intensive job. Any system developed is going to be only as good as the rnru .11111
    women who operate it. As one solid waste director of a major city said, “‘I’lli’ll I
    nothing more beautiful than watching my fleet of one hundred garbage 11111I
    leaving the yard silhouetted against the rising sun.”

    3-7 APPENDIX: DESIGN OF COLLECTIO

    N

    SYSTEMS

    Systems analyses can be used to design collection systems so as to minimize 1111
    cost of such systems. Consider the simple system pictured in Figure 3-26. ‘1111
    waste generated at four sources (denoted by centroids of the collection area, wi I I It
    is a poor assumption, especially if the disposal sites are close to the coll« 111111
    routes) is to be allocated to two disposal sites. The objective is to achieve this ill II
    minimum-cost manner.

    At the same time, several requirements must be met (constraints in an opil
    mization model).

    1. The capacity of each disposal site (e.g., a landfill) is limited.
    2. The amount of refuse disposed of must equal the amount generated.
    3. The collection route centroids cannot act as disposal sites, or the loll”

    amount of refuse hauled from each collection area must be greater 1It.lll
    or equal to zero.

    4. Total cost equals hauling cost plus disposal cost.

    Collection
    route centroids

    (source)

    ments of a simple solid waste management system.

    Iin VI1g notation is adopted:
    I,~ quantity of waste hauled from source i to disposal site k, per unit .tim
    f ,~ 0 t per quantity of hauling the waste fro~ source 1,to disposal sLt:eIt
    I~ disposal cost per waste quantity at disposal.slte k (cap.lta~plus operating]
    II~ apacity of disposal site k, in waste quannty per um,t H.me

    \ I total quantity of waste generated at source 1, per unit nme
    N number of sources i
    I’ number of disposal sites k

    I’lfillitllll then boils down to minimizing the following objective function:

    N ‘fXilh” + ± (F,,’fX;II)
    I 11,-] k= I ,=1

    I ~ I() th following constraints.
    C 1.11t raint 1. The sum of all the solid waste hauled out of each, section ?f the
    I 1111 ~ 111unity must be equal to or less than the capability of the disposal sites to
    II I Iv that waste, or

    N

    X;II :S E” for all k
    / I

    1I.IHraint2. The sum of all the waste hauled from a sectio? of the c~mmll-
    IIIy (to any disposal site) has to equal the amount generated m that secnon. or

    K

    Xik = W; for all i
    /i-I

    ‘onslr,IIIL . ‘I’ll’ w.ISI ‘ h.iu] xl OUI 11,\. I( Ill’ po. IIVI’ (Il()l II ‘H,Illv ‘), III

    Xiii ~ ° for allf, u
    The first term in the objective function is [ran p rtati n su and III ‘111’11111,1

    :erm is disposal costs. For the case shown in Figure 3-22, the I j IiV(‘ rill\( 11111
    Minimize [xnclI + X21C21 + X31C31 + X41C4\ + xlil2 + XnC22 -I- x,) ”

    + X
    42

    C
    42

    + FI(xn + X21 -I- X3\ + X41) -I- P2(X12 + Xl)
    + X32 + X42)]

    subject to the following constraints:

    Xli + X21 + X3\ + X41 S BI
    X
    21

    + xn -I- X32 + X42 S B2
    XlI + X21 + X31 + x4\ = WI
    XI2 + X22 + X32 + X42 S W2
    XlI ~ 0, XI2 ~ 0, … , X23 ~ 0, X24 ~ 0

    This problem can be solved using any linear programming algorithm. The 1,,111
    ~ortation algorithm is particularly useful for such applications.

    Assume the solid waste generation and disposal figure for the system
    pictured in Figure 3-26 is as follows.

    Cost of Transport, Cik
    Generation, Wi To Site 1 To Site 2

    Source; (tonnes/week) ($/tonne) ($/tonne)

    I 1 100
    5 12

    2 130 7 5
    3 125 4 8

    ~ 4 85 13 6

    Disposal Site, k Capacity, e, Cost, Fk($/tonne)
    1 450 4
    2 200 6

    We can hand calculate the cost for any option. Suppose all of the
    waste was to be sent to disposal in site 1 (h = 1). The cost for deliver-
    ing the refuse from the first source (i = 1) is

    100 tonnes/wk X $5/tonne = $500/wk

    th r ti n ,th ost w uld e $910, $ 0,
    I cost of $3015/wk.

    /wk X $4/ton = $1760/wk
    II, It I I co t is therefore $4775/wk.

    I hi i only one solution, and it might not be the least-cost
    111111 }11. find the least-cost solution (minimize cost), we can use

    iiI 11111 ort tion algorithm and find the following:

    II I To Disposal Waste Hauled Transport Cost Disposal Cost
    I II Site k (tonnes/week) ($/week) ($/week)

    1 100 500 400
    1 25 175 100
    2 105 525 630
    1 125 500 500
    2 85 510 510

    I” r fore, the total system minimum cost is $4350/week, substan-
    II Illy I ss than if all the refuse were shipped to disposal site 1. Note
    I111I considerable capacity remains unused in landfill 2.

    I ‘I1lS in which transfer stations are used also can be optimized by sys-
    tlll,liy is, using the scheme introduced previously. Figure 3-27 shows the

    I II r ummunity with four sources of waste and two disposal sites, but now
    III I ‘I’ station is placed in the town. The trucks now have K disposal points

    I I I ,II rrnediate facilities. As before, these facilities have processing costs and
    111htll~ id capital, plus operating costs. F. is the annual cost for the transfer sta-

    ] .
    111 , 1111 I P” is the annual capital and operating costs for the disposal sites. The
    111 I vnriables are

    “}= cost per quantity of hauling the waste from source i to intermediate
    facility j

    }”= cost per quantity of hauling the waste from intermediate facility j to
    final disposal facility k

    Xy = quantity of waste hauled from source i to intermediate facility j, per
    unit time

    X’I = quantity of waste hauled from intermediate facility j to final disposal
    facility h, per unit time

    Bj = capacity of intermediate facility j, in waste quantity, per unit time
    Pj = proportion of waste at intermediate facility j that, after processing,

    remains for disposal (P. = 1.0 if the facility is a transfer station, but
    ]

    P. = 0.2 if it is an incinerator)
    ]

    J = number of intermediate facilities j

    This objective function is subject to the following constraints: I I
    . f aste generated at source i, W, must equa I 11

    Constaint 1. The quantity 0 w to the J intermediate sites allll
    sum of all the waste hauled from that source
    K disposal points.

    ) K . .

    “‘x + ‘” x = W for aU1~ ik ~ III 1
    r= J 11=1

    . f the ith intermediate site, Bj, must be more than 01
    Constaint 2. The capacry 0 h J . If this constraint is omitted, the model
    equal to the total waste broug t t~ It. .
    can be used to determine the requIred capaoty.

    Add·lng transfer stations to the collection system plan.Figure 3-27

    . . . ize the following objective function:
    The problem now IS to rmrurn

    N K J K± iC,)X,) + ~~ClkXI11 + ~~lClkXIII
    i=lj=1

    J N K N

    + 2,Fj 2,xij + 2,FI/2,Xill
    j=1 ;=1 1/=1 1=1

    N

    ‘” x, :5 B. for all j.t:’…J ‘/ I
    1 I

    =

    Ih I JlI S 811 f rail k
    I I

    ” .\ I I II. what ver waste is shipped to an intermediate site I11USI hc : Ilippl’lI
    III III II III. lOSt I site. The proportion of waste that remains f r dispo: ill .IfII’1

    IIIH I’dllng i d noted by Pr
    N

    I’, ,1″/
    , I

    /(

    :2’>jll = 0 for all j
    1/-1

    III hi 111 ~. The nonnegativity constraints are

    0; XIII ~ 0; xjk ~ 0 for all i, j, k

    PPENDIX: POTENTIAL SOLUTIONS
    THE PROBLEM OF LITTERING

    I Ii wi, S towns have littering problems. Because tourism is an important ceo
    It I lor ill Switzerland and because the country is known for its deann ss, IIH’
    III pi )11 m has caught the attention of the authorities. The Swiss Federal mn’

    I. I IIV I’ nment has noted that the greatest litter problem occurs in city enters.
    lit ~ lilt ring problem requires targeted actions at a local level, which l11C1k(‘s

    11111111 LO carry out national measures. In Switzerland various combinations of’
    I 1111′ adapted to the local circumstances are being pursued, such as:

    1,,1111111 lion and Awareness-Raising Campaign
    I” III • d ily struggle against littering, it is essential to keep the public inform -d
    III 110 I’ ise awareness about the problems of littering and about the corr ct way
    II I dl .11 with potential items oflitter such as cigarettes, take-out food packagi IIg,
    111111, packaging, free newspapers, and chewing gum. This can be put into prnr

    II. II, ing advertising posters, newspaper advertisements, anti -litter am bassado rs,
    .” II ntly organized paper rubbish campaigns in the community and parishes.

    III1 lltter posters can be ordered free of charge in all three national languages
    1111111 the Interest Group for a Clean Environment (Interessengerneinschaft (‘Or

    1111′ s ubere Umwelt-IGSU) or from the Summit Foundation. Communitlr:
    u.l rowns may also book without cost and for a limited time, anti-litter arnbns
    111m from the IGSU for litter-intensive events or cleanup of public places.

    luturrnation and Education
    I III ‘ important measure against littering is education about the environment ill
    I II) Is, because the correct way to deal with waste cannot be learned early enough.

    J, C()(\~,of I\l-havlol’ f(1I 11ll’ Rtlull Sl'(‘~c)I’ uml SI)(‘dlll(‘lI (:ollln\(‘1 fell I
    Newspapers
    With the Code of i3ehaYior the retail outlets selling rake-out f()()d IlHII(I’ ,I \’TI
    untary commitment to supporting the communities in the flglu agaln/H 1111(
    The Code regulates responsibilities and defines the cooperation bCIW(‘t’lI 11\/11
    outlets and event promoters on the one hand (without regard to tlw sl~,I’ r r] 1111
    retail outlet or the scope of the event) and the local authori Iics Oil I III’ II( II
    hand. On this basis anti-litter measures can be implemented in puhlh Id,lI
    on an amicable basis. With regard to free newspapers dropped in puhlir ,III ,
    there are several initiatives between the cities (and communities) a nd IIII III
    newspapers. A model contract, which includes a list of specifications for III1 III
    newspaper publishers and distributors, is offered by the Swiss Federal Ofli •• 1111
    the Environment as a guide to help communities achieve transparent, 111,11111111
    agreements in the fight against free newspaper litter.

    4. Financial Incentives for Consumers
    For events that take place in a clearly defined area, a deposit on recyclable pilI I
    aging such as plastic bottles or reusable cups increases the rate of rcuu n ‘”hl
    reduces litter. This knowledge has been gathered and documented at v.ulnl]
    public events in recent years.

    5. Sanctions
    Awareness-raising measures can make sense in relation to certain PO))III.IIIIIII
    groups, but with some groups they have no effect. In these cases, sanctions ‘111111
    as fines may be considered. Some cantons and cities, of which the Canioux It!
    Thurgau, Solothurn, and St. Gallen and the City of Berne were the first, p,I’I~1Ii
    anti-litter laws that included fines for those caught littering. Other cities, lill\~
    ever, deliberately avoided laws that included fines for littering because it 1,111
    be difficult to enforce the law. The lack of a uniform approach has been IllIi
    troversial.

    References

    1. Unit-Based Pricing in the United States: A
    Tally of Communities. 1999. Washington,
    D.C.: EPA.

    2. U.S. Department of Labor, Occupational
    Safety and Health Statistics
    Department. 1998. Washington, D.C.
    As reported by Waste Age (July): p. 20.

    3. Getting More for Less; Municipal Solid Waste
    and Recyclables Collection Workbook.
    1996. Washington, D.C.: Solid Waste
    Association of North America.

    4. DeWeese, A. 2000. “Mandates Motivate to
    Automate.” Waste Age (February).

    5. Greenberg, M. R., et al. 1976. Solid Waste
    Planning in Metropolitan Regions. New

    Brunswick, N.J.: The Center for Urh,11I
    Policy Research, Rutgers University.

    6. Liebman, J. c.. J. W. Male, and M.
    Wathne. 1975. “Minimum Cost ill
    Residential Refuse Vehicle Routes.”
    Journal of the Environmental
    Engineering Division, ASCE, v. 100,
    n. EE 3:339-412.

    7. Kwan, K. 1962. “Graphic Programming
    Using Odd or Even Points.” Chinese
    Math. 1:207-218.

    8. Shuster, K. A. and D. A. Schul. 1974.
    Heuristic Routing for Solid Waste
    Collection Vehicles. EPA OSWMP
    SW-113. Washington, D.C.

    {U’I\\I,.n+ions U

    IIIVIIIIlIIIII’III,tll’IIIII’1 III

    Iq”‘p t\lill’II(‘;1 Ik.Ili1I1III,
    1110111’1 htls Wi OV(‘IY/,1(II

    /)I’II’llIilll\’ Ilit, lillll’ 11’1/\:
    pit’ll’ ” ill/litH dlld l’lllpl
    I II’/II,~(‘ 11)11(‘1 Iltlll vI’lill

    MEE 5901, Advanced Solid Waste Management 1

    Course Learning Outcomes for Unit II

    Upon completion of this unit, students should be able to:

    1. Assess the fundamental science and engineering principles of solid waste management.

    6. Relate leadership and management principles to effective solid waste management.

    Reading Assignment

    Chapter 3:
    Collection

    Unit Lesson

    There are four broad kinds of wastes that make up municipal wastes: municipal solid waste from residences,
    commercial business locations, government institutions and industry; yard wastes; recyclables that are
    processed to reenter commerce with a renewed purpose and function; and construction debris. All of these
    categories are non-hazardous wastes approved for handling, processing, and disposal in municipal landfills.
    When it comes to hazardous wastes from commercial businesses (e.g., spent solvent and process streams)
    and from households (polychlorinated biphenyls [PCBs] in florescent fixture ballasts, oils, paints, mercury,
    lead acid batteries, radioactive material, etc.), these must be separated out of municipal wastes to protect
    transporters, workers handling and processing municipal wastes, and the microbial populations that exist in
    municipal landfills tasked to convert organics to carbon dioxide and methane.

    The management of municipal solid waste begins with the collection of waste at the locations where these
    wastes are generated. When a municipality sends out bids for selecting and purchasing garbage trucks, there
    are many options in that marketplace to consider. For residential collections, trucks that are automated, semi-
    automated, or rear-loading work well. The choice will depend on the type of collection containers used and
    the number of employees working on each truck. If the containers are uniform in size and placed on the
    street, an automated truck with a single driver will be able to complete the collection; whereas, semi-
    automatic trucks require workers to bring the containers to a hoist located on the side of the truck. The third
    option involves rear-loading trucks that are manually operated. In some smaller communities, garbage trucks
    are divided to include recycling and refuse. When it comes to collecting waste from commercial locations,
    front loading trucks that have the capability to pick up bins with a set of front-end forks are mostly used. For
    larger commercial operations, roll-off compactors are the prime means for collecting non-hazardous wastes.

    Between the point that waste is collected and its disposal at the municipal landfill, there are some operations
    that can be used to help segregate and stabilize the different classes of waste. There are compost piles that
    are operated to stabilize materials high in organic content such as yard and food wastes. Compost piles
    operate aerobically, and the microbes rapidly degrade the wastes to generate a mix that can serve as a soil
    conditioner or as fill at the municipal landfill. What the compost pile is able to accomplish in one year can take
    a landfill from 10 to 30 years to provide the same level of stabilization. A second option is to use a facility
    known as a transfer station. These operations have many purposes: to compile waste collections into larger
    quantities for long-distance shipment to a landfill disposal sites, to pull out recyclable and hazardous materials
    that should not go into municipal landfills, to provide a hazardous waste drop-off point for citizens or to drop
    off wastes that need to be processed prior to going to the landfill, and to hold wastes in a safe location if the
    final disposal site cannot be accessed for reasons such as adverse weather.

    In large municipalities, waste transfer stations are a normal part of the municipal solid waste management
    plan for a community (United States Environmental Protection Agency, 1999). These facilities are often
    designed and operated to recover metals, paper, and plastics. Materials that are pulled out at the transfer

    UNIT II STUDY GUIDE

    Collecting and Handling
    Municipal Solid Waste

    MEE 5901, Advanced Solid Waste Management 2

    UNIT x STUDY GUIDE

    Title

    station are consolidated and shipped to a materials recovery facility that further segregates out different
    categories of materials. The higher the level of the sort, the higher the price that is paid to the recovery facility
    by the downstream customer taking in the sort as a raw material to its operations. Transfer stations are able
    to remove hazardous materials that are identified in the waste collection. All this recovery results in a reduced
    quantity of material going into the landfill, which extends the life of the municipal landfill before it must be
    capped and closed.

    Transfer facilities bring flexibilities to local communities by being a buffer between the generator of the waste
    and its final disposition. After the local landfill is filled and closed, the transfer facility is able to repurpose itself
    to facilitate the shipment of wastes to other landfills throughout the state or country. It is not uncommon for
    communities to put waste into rail cars and send these to a neighboring state while the local government
    works out a long-term solution. Looking at the economics of transport, it generally costs about $0.43/mile
    (United States Environmental Protection Agency [EPA], 2002) for each ton of waste that is shipped to a
    distant site when the trip is made by the local garbage truck. On top of this is the added salary of the workers
    making the trip with the truck and the increased cost of maintenance and depreciation of these trucks.
    However, if the waste is consolidated into large long-haul vehicles, the cost is reduced to $0.14/ mile (EPA,
    2002) for each ton of waste hauled to a distant location using one driver for the trip.

    In 1991, regulators responsible for permitting landfills began to mandate that federal criteria be used in the
    design and assessment of new landfill facilities (EPA, 2002). Municipalities that had previously operated older
    landfills found the costs of bringing a new landfill facility online to be exorbitant. By aligning with other local
    communities, it is generally very attractive to develop and permit a regional facility. Not only does this spread
    out the costs among many parties, but it also reduced the number of employees on the city payrolls. Regional
    landfills can also become profit centers by selling disposal capacity to rural communities and to municipalities
    unable to have their own local landfill. Regional facilities also help municipalities to attract new businesses
    and investments into the community. Having an adequate and well-functioning infrastructure is one of the key
    decision criteria that corporations use when selecting a community for their headquarters or
    manufacturing/distribution facilities.

    Many citizens operate by the out of sight, out of mind principle meaning that if they cannot see it, they do not
    think about it, and few give any thought to how waste is collected, processed, and disposed. However, when
    cities begin to construct and operate transfer stations, many of these same citizens begin to operate by the
    not in my back yard (NIMBY) principle, which means that they oppose the construction because it is close to
    them. Due to the fact that many transfer stations were being located in high-density, low-income areas, over
    the years the Environmental Protection Agency (EPA) received many complaints due to noise, odors, litter,
    and the large volume of heavy trucks passing through their neighborhoods. The National Environmental
    Justice Advisory Council (NEJAC) was formed in 1993 to provide the EPA with an independent voice related
    to the matters of environmental justice raised by affected citizens. The NEJAC provides the EPA with social,
    political, and geographical recommendations that addressed these complaints and provided the EPA with a
    basis for publishing criteria to be considered when designing and operating these facilities.

    United States Environmental Protection Agency. (2002). Waste transfer stations: A manual for decision-
    making. Retrieved from https://www.epa.gov/sites/production/files/2016-
    03/documents/r02002

    References

    United States Environmental Protection Agency. (1999). Municipal solid waste landfills, volume 1: Summary

    of the requirements for the new source performance standards and emission guidelines for municipal
    solid waste landfills. Retrieved from https://www3.epa.gov/airtoxics/landfill/lf-vol1

    MEE 5901, Advanced Solid Waste Management 3

    UNIT x STUDY GUIDE
    Title

    Learning Activities (Non-Graded)

    Practice the skills learned in this unit by answering the following questions:

    1. The landfill of a local municipality is filling to capacity, and the city is looking for ways to extend the life
    of the facility until a new landfill can be constructed and permitted. The city has hired you to look at
    two options to cover the transition period: (a) construct a transfer station with the idea of shipping the
    waste out of state, or (b) construct a mixed–waste-materials recovery facility and continue using the
    local landfill. In a table, do a side-by-side comparison of the facilities and then analyze these
    differences to make a recommendation to the city council as to which option you are recommending.
    Explain the criteria and rationale that you used to come to your recommendation.

    2. Not all wastes can be recycled or reused, especially when there are no post-consumer markets.

    Describe the ways that municipalities are seeking to implement a Zero Waste program. Describe
    three challenges when these programs are implemented, and propose a solution for each.

    3. A community is experiencing a serious litter problem from local citizens. The city council has hired

    your firm to propose a program to be implemented. Design a community program that addresses the
    causes and reasons for the litter problem. Show how the program will incorporate citizen education
    and awareness. How will the program hold citizens accountable when they continue to litter after the
    program is launched?

    4. Define the key elements that go into designing a refuse collection route. Which of the elements

    accounts for the most time in the collection of residential trash? What is your proposal to bring more
    efficiency into the design of the collection route?

    Non-graded Learning Activities are provided to aid students in their course of study. You do not have to
    submit them. If you have questions, contact your instructor for further guidance and information.

    I

    CSU Math Center | 1-800-977-8449 x6538 | teamsucceed@columbiasouthern.edu

    Math Center Requests: Math Center Request Form

    Municipal Government &

    Transfer Station

    Problem: A municipal government has agreed to provide once per week waste collection services to a

    new residential community of 25,000 people. The city council has hired you to make a preliminary
    assessment to determine if they should build and operate a transfer station to support the collection.
    For the initial analysis, assume that the community does not have a recycling program. Here is some

    of the initial data that the municipal engineer has collected.

    * The round trip distance from the residential community to the landfill is 40 miles.
    * The size of the residential garbage truck that collects waste from the community is 30 cubic yards.

    * The round trip distance from the proposed site of the transfer station will be 45 miles.
    * The garbage truck is capable to compact the refuse to 700 lbs./yd3.
    * A long haul truck is capable to transport 25 tons of compacted waste per trip.

    * The transfer station has a fixed operating cost of $15/ton.
    * The cost to operate the garbage truck is $1.50/mile.

    * The cost to operate the long haul truck is $0.75/mile.
    (a) Would you recommend to the city council that a transfer station should be built and operated?
    Show all work on how you came to your answer.

    * The United Nations estimates waste generation rate is 4.8 lbs. per person per day.
    (See page 39 of the textbook)

    (b) If the community operated a recycling program, would this change or support your

    recommendation to the city council? Show all work on how you came to your answer.
    * Total recycled municipal waste is 33.2% of generation.

    Solution:

    (a) We will use the estimated waste generation rate of 4.8 lbs. per person per day in this calculation.

    Step 1
    Residential waste generated = 25,000 people x 4.8 lbs. x 7 days = 840,000 lbs. or 420 tons

    person/day 1 week each week

    Step 2
    Calculate the waste collected in each truck:

    30 yd3 x 700 lbs. = 21,000 lbs. of waste collected per truck

    truck yd3

    Step 3
    Calculate the number of trucks needed:

    840,000 lbs. = 40 trucks (round up)
    21,000 lbs./truck

    Step 4

    Determine the cost to travel to landfill by garbage trucks:

    40 trucks x $1.50 x 40 miles = $2,400 per week
    week mile

    mailto:teamsucceed@columbiasouthern.edu

    https://mycsu.columbiasouthern.edu/student/forms/courses/math-center-request/

    Step 5
    Calculate the number of long haul trucks based on residential waste generated:

    420 tons = 17 trucks (round up)
    25 tons per truck

    Step 6
    Determine cost to travel to transfer station by long haul trucks:

    17 trucks x $0.75 x 45 miles = $573.75
    mile per truck

    Step 7
    Calculate cost of transfer station:

    420 tons x $15 = $6,300

    ton

    Step 8
    Calculate cost by long haul truck:

    $573.75 + $6,300 = $6,873.75

    Therefore, the community should not build and operate a transfer station. Doing so will increase
    costs by :
    $6,873.75 x 100 = 286% or 186%* higher cost

    $2,400.00

    * 286%  100% = 186%

    (b) We will use the total recycled municipal waste generation of 33.2%. This also means that 66.8%
    of waste goes to the landfill per total waste that is generated. We will also use the estimated

    waste generation rate of 4.8 lbs. per person per day in this calculation.

    Step 1
    Calculate residential waste generated:

    25,000 people x 4.8 lbs. x 7 days x 0.668 = 561,120 lbs. or 281 tons

    person/day week (round up)

    Step 2
    Calculate the waste collected in each truck:
    30 yd3 x 700 lbs. = 21,000 lbs. of waste collected per truck
    truck yd3
    Step 3
    Calculate the number of trucks needed:

    561,120 lbs. = 27 trucks (round up)
    21,000 lbs./truck

    Step 4
    Determine the cost to travel to landfill by garbage trucks:

    27 trucks x $1.50 x 40 miles = $1,620 per week
    week mile

    Step 5
    Calculate the number of long haul trucks based on residential waste generated:

    281 tons = 12 trucks (round up)
    25 tons per truck

    Step 6
    Determine cost to travel to transfer station by long haul trucks:

    12 trucks x $0.75 x 45 miles = $405.00
    mile per truck

    Step 7
    Calculate cost of transfer station:

    281 tons x $15 = $4,215

    ton
    Step 8
    Calculate cost by long haul truck:

    $405 + $4,215 = $4,620

    No, implementing recycle programs still leads to the collusion that the community should not build
    and operate a transfer station. Doing so will increase costs by:

    $4,620 x 100 = 285% or 185%* higher cost
    $1,620

    * 285%  100% = 185%

    MEE 5901, Advanced Solid Waste Management

    Unit II Assignment

    This assignment will allow you to demonstrate the following objectives:

    · Assess the fundamental science and engineering principles of solid waste management.

    · Relate leadership and management principles to effective solid waste management.

    Instructions: In this unit, the management of municipal solid waste starts to be viewed from the perspective of the local government. This involves looking at questions that need to be answered to properly develop waste management policies and practices for the community. Some of the economic aspects of waste management are explored, as all these activities need to be funded and budgeted and paid for by the community.

    Answer the questions directly on this document. When you are finished, select “Save As,” and save the document using this format: Student ID_Unit# (ex. 1234567_UnitI). Upload this document to BlackBoard as a , docx, or .rtf file. The specified word count is given for each question. At a minimum, you must use your textbook as a resource for these questions. Other sources may be used as needed. All material from outside sources (including your textbook) must be cited and referenced in APA format. Please include a reference list after each question.

    1) Describe three key factors that help to determine the likelihood that a person will litter. Which of these factors is most likely to contribute to the probability that a person will litter. State how you came to this conclusion.

    To fight litter in your community, design a six- step actionable litter plan that you can give to a project team to implement. In your plan, include the management principles that go into making this plan. Justify to the implementation team why your plan will be successful. (Your total response for all parts of this question should be at least 300 words.)

    2) A municipal government has agreed to provide once- per- week waste collection services to a new residential community of 10,000 people. The city council has hired you to make a preliminary assessment to determine if they it should build and operate a transfer station to support the collection. For the initial analysis, assume that the community does not have a recycling program. Here is some of the initial data that the municipal engineer has collected. The round- trip distance from the residential community to the landfill is 58 miles.

    · The round- trip distance from the proposed site of the transfer station will be 63 miles.

    · Size The size of the residential garbage truck that collects waste from the community is 28 cubic yards.

    · The garbage truck is capable to of compacting the refuse to 650 pounds per cubic yard.

    · A long- haul truck is capable to of transporting 23 tons of compacted waste per trip.

    · The transfer station has a fixed operating cost of $10/ton.

    · The cost to operate the garbage truck is $1.30/mile.

    · The cost to operate the long- haul truck is $0.56/mile.

    a) Using what you have determined from the information above, assess using the principles of solid waste management. Would you recommend to the city council that a transfer station should be built and operated? Show all work on how you came to your answer. Note: Pg.p. 39 – The United Nations (UN) estimates the waste generation rate is 4.8 pound per person per day.

    b) If the community operated a recycling program, would this change or support your recommendation to the city council? Show all work on how you came to your answer. Note: Pgp.. 99 – Table 3.-1 – total Total recycled municipal waste is 34.5% of generation. (Your total response for all parts of this question should be at least 200 words.)

    3) Phase 1 of the refuse collection system discusses volume-based fee systems and weight-based fee systems.

    a) For a residential community, explain why a volume-based fee system would be recommended.

    b) Give the reasons for the fee based system that you would recommend for a commercial operation.

    c) For a construction site, defend your recommendation for the fee based system that you would recommend.

    d) What leadership and/or management principles factored into your recommendation? (Your total response for all parts of this question should be at least 200 words.)

    4) Table 3.-1 (pg.p. 99) is a listing of materials collected in recycling programs in 2012.

    · Which of these would you recommend to go to a compost pile? What percent of the 2012 recycled materials does this divert?

    · Provide your recommendations to the city council for how you would keep materials destined for composting from comingling with the other recycled materials. (Your total response for all parts of this question should be at least 200 words.)

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