HomeMy WebLinkAbout9.F.2. Dick's Sanitation Proposal for One Sort Recycling CITY OF SHAKOPEE
Memorandum
TO: Mayor and City Council
FROM: Mark McNeill, City Administrator
SUBJECT: Dick's Sanitation Proposal for One Sort Recycling
DATE: June 5, 2012
Comment:
Introduction:
The Council is asked to consider a proposal from Dick's Sanitation Inc., for a one sort
recycling option for its Shakopee residents.
If approved, it would involve require a negotiation of an extension of the current Dick's
contract.
Background:
Dick's Sanitation has been the City's designated garbage and recycling hauler since
2001, which was the last time competitive quotes were taken. A five year contract
extension was negotiated for renewal in 2006. In 2010, the Council extended the existing
contract for an additional three years, in exchange for a reduction in garbage and
recycling pick up rates. The existing contract runs through May 31, 2014.
Dick's has approached the City with a proposal to change the method in which recycling
materials are collected. In this, they propose to convert to a "single sort" system, wherein
all recycling would be placed by the customer into a wheeled container, which would be
nearly identical in design to the garbage containers currently used.
The single sort system is becoming more widespread, and is seen favorably by many
customers in that it eliminates the need to separate recyclables, and to bundle cardboard
and newspapers. It also offers the advantage of eliminating the debris caused by wind-
blown materials, in that the recyclables are kept in a covered container.
However, more of the recycled materials may become contaminated in the single sort
system, and therefore must be incinerated or landfilled at a higher disposal cost, and cost
to the environment. However, Dick's does indicate that the overall participation in
recycling is greater in a single sort system, thus offsetting some of the loss of the
contaminated materials. In most cases, the single sort system actually increases the
amount of recyclables diverted from the waste stream.
It should be noted that recycling does impact the cost of providing garbage services; the
economy has a major impact on the market for recyclables. When the economy was
strong, Dick's reported that they would often sell Shakopee recyclables at $30 per ton.
The City received a portion of that amount back, which went towards off - setting the cost
there were times when Dick's had to actually pay to have recyclable materials taken.
However, regardless of the recyclable materials market, it usually still makes economic
sense to recycle —the cost of incineration is usually more expensive per ton.
As shown in the attached letter from Dick's Sanitation representative David Domack,
Dick's proposes to go to a single sort system, but indicates that it would be an investment
of $1.4 million for the new carts. To do this it proposes to extend the existing contract by
5 years from the current May 31 2014 expiration date.
Analysis:
It is apparent that the industry is moving towards a single sort system, and the option is
very popular with customers. Therefore, it would be widely seen as a service
improvement to go with this sort of system. However, part of the increase in efficiency is
that instead of recycling be picked up weekly as it is now, it would be done every other
week. That change does affect the City as well, in the positive terms of there being less
wear and tear on the streets, but customers will have to pay more attention to
scheduling —if they miss their recycling day, they will have a month's worth the next
time that recycling is collected.
Related to this, the City Council has also had previous discussion about the need to be
assured that the best possible rates are being extended to Shakopee customers covered
under the City's organized collection contract. At the end of the current contract, it will
have been fifteen years since competitive quotes were last taken. Staff sees Dick's
Sanitation as being responsive to needs and customer service, but there may be an
alternative provider who could do as well or better. The City does get frequent calls from
other providers who inquire as to when the current contract expires.
If the Council chooses to accept the single sort proposal now and thus extend the current
contract, it should direct Dick's to come back with a more concrete disposal, including
providing staff with what the rates would be for the five year extension of time.
On the other hand, if the Council wishes to seek bids for a new contract after the current
one expires, sufficient time will need to be provided to put together contract
specifications, allow for a solicitation of a Request For Proposals, and award the contract
in time so that any newly - designated hauler may order the garbage and recycling carts in
sufficient quantities to service 11,000 accounts. The lead time for that is months; it would
mean that RFP's should be sent out early in 2013.
Whenever garbage services are discussed, it could also be expected that a discussion of
the philosophies of "organized" versus "open" systems might be heard. Shakopee has had
the organized system for as long as anyone can remember, and seems to have served the
City well -there is less wear and tear on streets, and overall rates seem to be lower than in
neighboring cities with comparable services, due to the greater efficiencies provided by
the organized system. Organized collection makes it much easier for the City to comply
with State law which mandates curbside recycling for all its customers. Finally, organized
collection discourages illegal dumping of waste by residents and businesses, as customers
are paying for the service anyway.
Alternatively, the open system is popular with people who prefer to hire their own
haulers.
David Domack of Dick's Sanitation will be present at the June 5 meeting to more fully
discuss the single sort proposal. See the attached letter.
Alternatives:
1. The Council accepts the Dick's Sanitation proposal, and directs the staff to
negotiate rates for a five year extension.
2. Reject the proposal, and direct that staff prepare to issue a Request for Proposals
for garbage and recycling services for the five year period to commence June 1,
2014. Note that by rejecting the single sort proposal, it would mean that
Shakopee will need to continue with the current two sort "bin" recycling system
for the remainder of the current contract.
3. Table for further information.
Recommendation:
I recommend item 2 above, which directs staff to prepare an RFP for a provision of
garbage and recycling services for a five year contract to commence June 1, 2014. This
RFP would come back to Council for further direction before it would be issued.
Relationship to Visioning:
This supports Goal A — "Keep Shakopee a safe and healthy community where residents
can pursue active and quality lifestyles."
Action Required:
Council should hear the proposal, discuss and provide direction as to the prevision of
recycling, and garbage, services in Shakopee.
lyt
Mark McNeill
MM:cn City Administrator
rDSI) Sanitation Inc.
May 21, 2012
Mark McNeill
City of Shakopee
129 Holmes Street South
Shakopee, MN 55379
Dear Mark McNeill, Mayor and Members of Council,
Dick's Sanitation, Inc. appreciates serving your community with quality trash and recycling services over the past twelve
years.
Over this period of time, our industry has seen advances in new technology. One of the biggest advancements has been in
the way that we can accept, collect and deliver recycling materials to markets — which is better know as "one- sort" recycling.
One -sort recycling allows us to collect your recycling materials all mixed together in a residential cart. The one -sort program
provides convenience, less traffic on the streets (due to the every other week collection) and people recycle more.
Due to the financial commitment associated with converting to one -sort recycling of an estimated $1.7 million dollars. Dick's
Sanitation, Inc. is requesting the opportunity to enter into renegotiations with the City of Shakopee for a five year extension
of our existing agreement.
The extension would allow us to absorb the additional equipment costs incurred to implement one -sort recycling without
increasing our rates to the residents of Shakopee.
Dick's Sanitation, Inc. has developed a full - service program to satisfy all of your community's needs. We are confident that
this one -sort recycling program will enhance the quality and value your residents have enjoyed over the past several years.
Thank you for your consideration.
Sincerely,
anid smack
David Domack
V.P. Sales & Marketing
Dick's /Lakeville Sanitation, Inc.
david@).dickssanitation.com
952- 469 -9870
Dick's Sanitation Inc.
8984 215th Street West Lakeville, MN 55044
Phone: 952 - 469 -2239 Fax: 952 - 469 -1146 WWW.dickssanitation.com
Cit of Minnea•olis
Dual Sort /Single Sort Collection St..
..t -'May 10, 2012
416 Longshore Dr. 1 Ann Arbor, MI 48105 I 734.996.1361 p 1 734.996.5595 f 1 www.recycle.com
Report
Minneapolis SEH
City of Lakes
Resource Recycling Systems
-, ,.,44111r Sustainable Systems for a Waste -Free Future
Table of Contents
Executive Summary and Key Points 1
Introduction & Background 3
Solid Waste and Recycling Programs and Policies 4
Minnesota Solid Waste Management Tax 5
Waste and Recycling Infrastructure 6
Disposal Cost Summary 7
Comparative City Information 8
Changes in Collection Systems 10
Recycling Collection Options 10
Current Multi -Sort Collection Program 11
Dual -Sort Collection Program 12
Single -Sort Collection Program 12
Curb Container Set Out Options 12
Collection Assessment 15
Location: Alley vs. Curbside 15
Width and turning radius 15
Height Restrictions 15
Options 15
Pilot Collection Program 16
Focus Group Meetings 17
MEETING PARTICIPANTS 18
ATTITUDES TOWARDS PROGRAMS AND COMPARABLE EXPERIENCES 18
RECYCLING Carts and Bins 19
=,=a I RECYCLING AWARENESS AND EDUCATION 19
SPECIAL PROGRAMS and ADDITIONAL SERVICES 20
COMMENTS 20
Collection Options Analysis and Costs 21
Recycling Incentive Programs 23
Incentive System Pros and Cons 25
Pros 25
Cons 25
pad Processing Options 25
Secondary Markets 27
Markets and Revenue for Materials 27
General Discussion of Dual -Sort Recycling 29
Background on Dual -Sort 29
Dual -Sort Scale of Operations 30
Dual -Sort Sequence of Operation 30
General Discussion of Single -Sort Recycling 31
Background on Single -Sort 31
Early Single Sort Problems 32
Challenges 32
Improved Technologies 33
Single -Sort Scale of Operation 34
Sequence of Operation 34
uk
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Adding Materials to the Recycling Sort 36
Metals 36
Poly- Coated Fiber 36
Plastic Film 36
Large Rigid Plastics 37
Opimizing Sorting Choices 38
FINDINGS AND RECOMMENDATIONS 39
Appendices
Appendix I: Hennepin County Resolution 42
Appendix II: Revenue Projections 45
Appendix III: Dual Sort Process Flow Diagram 46
Appendix IV: Single Sort Process Flow Diagram 47
" Resource Recycling Systems
`. Sustainable Systems for a Waste -Free Future S E H
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EXECUTIVE SUMMARY AND KEY POINTS
The State of Minnesota has established new recovery goals for Hennepin County, which includes 45% recycling
rate by 2015 and 47% by 2020. Hennepin County has established a recycling goal of 35% for the City of
Minneapolis. The City of Minneapolis contracted a study and assessment of collection options and the impact on
the value of the marketable materials, to assist in determining its next steps.
The City operates a bi- weekly at- the -curb, multi -sort collection system, which requires residents to place all
items in separate paper bags in their recycling bin. Although the community accepts and supports recycling, for
more than 10 years the city has seen a stagnant recycling rate, and in some years, the rate has declined. The City
has a fairly good participation rate for the recycling program, yet compared to other cities in the region and the
nation; the amount of material recycled by residents is far below the regional and national average.
Minneapolis conducted two pilot programs, testing the effectiveness of dual -sort and single -sort collection. Both
pilot programs incorporated recycling carts and collecting on the bi- weekly schedule. The results from these
pilot programs show a significant increase in number of stops that can be served by a single route and the
quantity of recyclables collected per household.
Key Points from Recycling Program Study
The study findings, summarized below, are based on information collected from the city's pilot programs and
from the experiences of other cities, and from focus group meetings held with current Solid Waste and Recycling
customers. The project evaluated single -sort and dual -sort collection for both weekly and biweekly collection.
Recovery
1. A single -sort system is projected to increase materials quantity recovered by 60% and the Minneapolis
recycling rate increases from 18.1% to 32% (based on case studies such as Ann Arbor and Portland).
2. A dual -sort system is projected to increase materials quantity recovered by 36% and the Minneapolis
recycling rate increases from 18.1% to 25% (based on case studies such as Ann Arbor and Portland).
Processing
ESa K
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1. The majority of local recycling centers - Material Recovery Facilities (MRF's) - are well equipped to
handle single sort collection.
2. Preliminary research indicates no difference in market revenues — single vs. dual in local MRF's.
Operations and Operational Costs
1. Collection time for single -sort is less than dual -sort and there is no need to come off route when one
compartment fills before the other.
2. A single -sort recycling system preserves space for a possible third cart for comingled yard waste and
organics.
3. A semi - automated rear load truck (such as currently used for garbage collection), with 2 staff per truck,
best serves alley -based collections. This is the same system that is currently used for garbage collection.
4. Single -sort collection allows for utilization of a similar truck fleet to current rear load packers, resulting
in a more cost - effective fleet than adding a completely new type of vehicle for recycling collection.
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Capital Costs
1. Dual -sort collection requires an additional truck cost of $28,000 more than single sort truck due to split
body packers.
2. Cart cost for single sort (1 per unit @$65) is estimated at $6,800,000.
Truck Cost (8 trucks) for a bi- weekly single sort collection program is $1,976,000.
3. Cart cost for dual sort (2 per unit @$50) is estimated at $10,500,000.
Truck Cost (9 trucks) for a bi- weekly, dual sort collection program is $2,475,000.
Overall Program Costs
The Net Recycling Costs are the lowest for the Single Sort Semi Automated Bi- weekly collection program by
approximately 20% below current net cost while achieving a 32% recycling rate. The Dual Sort Bi- weekly
program has a net cost of approximately 65% higher then the current multi -sort program and achieves a 25%
recovery rate. A ten percent increase in the quantity of material collected in the single sort program achieves a
35% recycling rate with a net cost that is 40% lower then the current program. A ten percent increase in the
quantity of material collected in the dual sort program achieves a 28.5% recycling rate with a net cost that is
40% higher then the current program.
J
Single -sort collection and processing also allow consideration of transferring recyclables from milt - family
[ locations should Minneapolis be interested in offering recycling services in currently under - served areas. Single
sort collection programs are more compatible with the development of a yard waste and organics collection
program that would require another cart.
Although dual -sort recycling remains technically viable, when you consider that the market trend is toward
single -sort processing and that placing recyclables all in one container, which is the most convenient to most
residents, it is clear that Minneapolis should consider switching to single -sort collection.
It is further recommended that the City conduct a more detailed evaluation of the program and investment
requirements associated with such a conversion to single sort collection and processing by issuing a Request for
$' Proposal (RFP) to determine the actual collection and processing costs. This evaluation would include equipment
options and costs, processing and marketing arrangements, route requirements, and program investments and
savings.
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INT & BKGROUND
Many cities and solid waste districts throughout the nation are setting new, ambitious goals for higher recycling,
waste recovery rates and even targeting zero waste as an attainable goal.
The State of Minnesota has established new recovery goals for Hennepin County, which includes 45% recycling
rate by 2015 and 47% by 2020. Hennepin County Department of Environmental Services approved a Resolution
to establish recycling goals and revise the Funding Policy for recycling grants efforts, establishing a recycling goal
of 35 %. The goals stated in the Hennepin County Resolution are to increase recycling participation, increase the
amount of material recycled and reduce the cost of services. To meet those goals, Hennepin County is
' considering establishing what materials should be included in recycling programs and requiring implementation
of either dual -sort or single —sort collection. A copy of the Resolution is included as Appendix #1.
Minneapolis' curbside recycling program began as a pilot, monthly collection in 1982. Over the years, the
i number of items collected was increased in the program and the frequency of collection was shifted to bi-
weekly service. The collection method has remained as an at- the -curb, multi -sort system, which requires
residents to place all items in separate paper bags in their recycling bin. Although the community accepts and
supports recycling, for more than 10 years the city has seen a stagnant recycling rate, and in some years, the
rate has declined.
WI FIGURE 1: MINNEAPOLIS RECYCLING RATE AND HENNEPIN COUNTY RECYCLING GOAL*
— -Hennepin County Goal (Grant Requirement)
fMLPS Recycling Data
40%
35%
30%
25%
20% • • • • ■
15%
10%
5%
0% 1 1
2005 2006 2007 2008 2009 2010 2011
*2011 Recycling Rate = 18.1%
The challenge facing the City is how to increase the current recycling rate to meet the goals set by the State of
Minnesota and supported by Hennepin County, while providing a cost - effective program that can be embraced
by its residents and businesses.
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SOLID WASTE AND RECYCLING PROGRAMS AND POLICIES
Both state and local government policies play a strong role in shaping recovery in the TCMA. At the state level,
Minnesota's Waste Management Act (WMA) (Minn. Stat. §115A), enacted in 1980, establishes the following
program goals.
An official hierarchy of waste management methods:
(1) Waste reduction and reuse;
(2) Waste recycling;
(3) Composting of yard waste and food waste;
(4) Resource recovery through mixed municipal solid waste composting or incineration;
(5) Land disposal which produces no measurable methane gas or which involves the retrieval of
methane gas as a fuel for the production of energy to be used on -site or for sale; and
(6) Land disposal that produces measurable methane and which does not involve the retrieval of
methane gas as a fuel for the production of energy to be used on -site or for sale.
• A statewide source reduction goal to be achieved by December 31, 2000, of a minimum ten percent per
capita reduction from the 1993 MSW generation (Minn. Stat. § 115A.55).
A 50 percent recycling p y g goal for the metropolitan counties, including credits for yard waste and source
reduction, which can add up to 8 percent to the base recycling rate (Minn. Stat. 5 115A.551).
In addition, Minn. Stat. 5473.149 establishes requirements for comprehensive solid waste planning, including
• setting quantifiable objectives for reducing land disposal in the TCMA region. At the local level, the metropolitan
counties have the primary responsibility for creating this plan and managing the integrated solid waste system.
The 2008 Minnesota Climate Change Advisory Group (MCCAG)'s recommendations, which are not statutory
requirements, also guided the TCMA's solid waste planning process. These include statewide goals of 60
percent recycling and 15 percent organics recycling by 2025 to help reach greenhouse gas reduction goals set by
the legislature. The goals established for the metro area are shown in Table 1 below. Hennepin County adopted
the goals established by the MPCA in its Policy Plan adopted April 10, 2012 with the exception that the county
• has an organics recovery goal of 6 percent by 2015 and by 2020.
Table 1: Solid Waste Management Goals
• Source Reduction and Reuse (minimum) 1 -2% °
Recycling (minimum) 41% 45 -48% 47 -51% 48 -54% 53 -60%
Organics Recovery (minimum) 2% 3 -6% 4 -7% 5 -9% 7 -9%
Resource Recovery (expected) 29% °
y ( p ) 32 -34/0 34 -35/0 32 -33/0 29 -30%
Landfill (maximum) 28% 20% 15% 15% 11%
Residential recycling programs consist of curbside collection and drop -off sites, and include recycling services for
both single - family and multifamily housing. Curbside recycling programs in the TCMA are provided by haulers
through a contract with a municipality or are provided through subscription service. Most counties provide
k :! some funding for municipal programs. The private sector, municipalities, and two counties provide numerous
public drop -off locations for one or more types of recyclables.
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MINNESOTA SOLID WASTE MANAGEMENT TAX
The State of Minnesota also promotes recycling of waste via a Solid Waste Management Tax levied on all mixed
municipal solid waste management services. Services for recycling, yard trimmings and other materials
separated from the waste sort are exempt from the tax. This has a net effect of increasing costs of disposal and
decreasing the relative costs to recycle, thereby encouraging businesses and communities to recycle more. The
current Solid Waste Management Tax rates are:
• 9.75% for residential generators
• 17% for commercial generators and self - haulers
The City of Minneapolis tax is calculated and the tax incentive for recycling is shown in Table 2.
Table 2: Solid Waste Management Tax Example
Sample Tax: One residential dwelling
unit with a single large garbage cart per Calculation Non - Recycler Recycler
Base Fee $24.00 x 9.75 % = $2.34 $2.34
Recycling Credit $7.00 x 9.75% = ($0.68)
Cart Disposal Fee $5.00 x 9.75% = $0.49 $0.49
A
Total Tax $2.83 $2.15
¢ 4
r :
t
t.
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WASTE AND RECYCLING INFRASTRUCTURE ji
Several large incinerators, landfills, and material recovery facilities, as well as numerous transfer stations serve
the TCMA. These are shown are listed in Table 3.
Table 3: Disposal Infrastructure
Landfills:
Primary recipient of
Pine Bend Sanitary Landfill Inver Grove Heights, MN C &D, MSW 792 $70.00* TCMA landfilled
waste
SKB Rich Valley Demolition Landfill & TS South Saint Paul, MN C &D, MSW 5 N/A
Secondary recipient
Elk River Sanitary Landfill, Inc. Elk River, MN C &D, MSW 1503 $78.80* of TCMA landfilled
waste
Primary recipient of
Burnsville- Kraemer Sanitary Landfill Burnsville, MN C &D, MSW 1074 $69.78* TCMA landfilled
waste
Dawnway Demolition Landfill South Saint Paul, MN C &D, MSW 63 N/A
Lake Elmo- Washington County Landfill Lake Elmo, MN MSW NA N/A
Ruby Landfill Township Maiden Rock, WI MSW N/A N/A
Incinerators:
Elk River RDF Processing Facility Elk River, MN MSW 1664 $69.00
Refuse - derived fuel
processing
Converts MSW into
refuse - derived fuel,
NRG- Ramsey /Washington RDF Newport, MN MSW, Tires, Wood 1192 $50.00 ferrous and non-
ferrous metal
recovery
Mass -burn
Hennepin Energy Resource Company technology with
(HERC) Minneapolis, MN MSW 740 $47.00 ferrous metal
recovery
Transfer Stations:
C &D, MSW, Yard
Waste Management Transfer Station Saint Paul, MN Waste 324 $60.00
C &D, MSW, Yard
Twin Cities Recyco Transfer Station Blaine, MN Waste 312 $85.00
Richard's Transfer Station Savage, MN C &D, MSW 255 $43.00
C &D, MSW, Yard
Bellaire Resource Recovery System TS Stillwater, MN Waste 134 $50.00
WMI / Northern Wisconsin TS River Falls, MN C &D, MSW 100 $55.00
Dakota Resource Recovery, Inc. TS / Inver Grove Heights, MN C &D, MSW 63 $50.00
United Waste
Knutsen Services Inc. TS Rosemount, MN MSW 63 N/A
Freeway Transfer Station Burnsville, MN MSW, Tires (Auto) 819 $45.00
C &D, MSW, Yard
Hennepin County Recycling Center Brooklyn Park, MN Waste 595 $45.00
Cambridge SW Transfer Station Cambridge, MN C &D, MSW, Ash 136 $49.00
Minneapolis South Side Transfer Station Minneapolis, MN C &D, MSW 4 $88.92
• Tip fees shown are stated gate rates.
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• Table 4: Processing Infrastructure (Material Recovery Facilities)
Facility Location _Material Lines To S er,Ray ..,
Allied Waste Minneapolis Mixed Fiber, Commingled Containers
Recycling Center Minneapolis, MN (rigids), All Materials - single sort, High Grade 500
Fiber
Eureka Recycling St. Paul, MN Mixed Fiber, Commingled Containers 180
Inver Grove Heights /St. Paul Inver Grove Heights, All materials 200
(Allied Waste) MN
Mall of America - Waste and Bloomington, MN Commingled Containers, Mixed Fiber- 31
Recycling Department Manual, OCC- manual
Pierce County MRF Ellsworth, WI Glass- manual, Commingled Containers - no 16
glass, Mixed Fiber
Pythons of St. Cloud Inc. St. Cloud, MN Mixed Fiber, Commingled Containers, OCC 85
Recycle America Alliance Minneapolis, MN Mixed Fiber, Single Sort, Dual Sort 558
containers, OCC
A majority of local recycling centers — Material Recovery Facilities (MRF's) — have made significant capital
n
investment on single sort processing.
DISPOSAL COST SUMMARY
Table 5 contains estimates from the TCMA's solid waste plan for the all- inclusive cost per ton for various methods of
managing solid waste, taking into account recycling revenue, collection costs, processing costs, and tip fees. Where
possible, tip fees and collection costs have been disaggregated. Actual costs from the City of Minneapolis as well as private
hauling companies are used in the analysis of program costs.
Table 5: Estimated Costs Per Ton for Solid Waste Management
Management Method Total Cost Tip fee Collection and other costs
per ton
4 i Recycling (residential) $110 -$143 Not applicable Unable to separate these costs
r 71 Recycling (commercial, institutional, and industrial) $85 - $90 Not applicable Unable to separate these costs
Organics (Food to animals) $0 - $49 Not applicable Unable to separate these costs
Organics (SSO) $80 - $193 $40 - $45 $40 - $148
ill
1
Waste to Energy $168 - $207 $47 - $84 $119 - $123
Landfill $130 - $162 $39 - $43 $91 - $119
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COMPARATIVE CITY INFORMATION
The cities included in the comparative analysis that have single sort systems are Ann Arbor, Kansas City, and
Cincinnati. Keeping glass separate from the remainder of the recyclable materials modifies Kansas City's single
sort collection.
Table 6: Comparative Recycling Participation Rates
�. > ate.. . aid Recy 41 Ra
Current MPLS 18%
St. Paul 30%
Ann Arbor 37%
Portland 34%
Kansas City ** 16%
Cincinnati ** 18%
Communities that have converted to dual sort or single sort collection experience an immediate, significant
increase in the volumes collected. Residents do not have to provide as much space for sorting and storing
materials in preparation for their collection day, and find it easier to carry materials to the curb in fewer
containers. Further, the routes can be expanded to serve a larger number of stops, which saves in truck usage,
labor and travel time on the street. It has been demonstrated throughout the country that cart based systems
increases the amount of recyclable material that can be collected in a bi- weekly or weekly program.
Table 7: Comparative Recycling Quantity Rates
Recycling Collection Single Sort Dual Sort Single Sort Single Sort Single Sort
Weekly Weekly Weekly Biweekly Weekly
Container Cart Bin Bin Cart Cart
Lbs. /HH 726 477 302 386 659
The five comparable cities offer a variety of service combinations to consider. Each has its own success story.
Each has adapted to its own program, so additional review would be beneficial in evaluating which options
would be the most applicable.
Table 8: Comparative Recycling Changes
Ann Arbor Saw 15% increase in tonnage with switch from weekly dual sort bins to single sort carts
St. Paul
Saw 15% increase in tonnage with switch from source separated biweekly bins to dual
sort weekly bins
Saw participation increase from 40% to 71% with switch from weekly bins to biweekly
carts
Cincinnati
Switch saved city $900,000 per year
Tonnage increased by over 50% in same time period
F.�
tY
Carts versus bins: Carts have consistently shown an increase in the volume of recycling collected. Carts offer
greater capacity, more stability and decreased risk of materials becoming wind - strewn or placed in trash when
the bin is full before collection. There are concerns, as noted in the later section entitled 'Curb Set Out Options',
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about the size of the carts and difficulty in handling to the curb. However, with consistent, user - friendly
education and if carts are offered in size options, carts yield greater participation and volumes.
Waste versus recycling: The combination of waste and recycling collection remains a factor in recovery rates. If
unlimited waste disposal, at a low rate of cost is offered to a community, it is very easy to put everything into a
waste container. Successful programs focus on discouraging waste disposal and encouraging recycling,
composting and source reduction as the better alternatives. This can be accomplished through education and
encouraging participating in the recycling programs and through the variable pricing of waste disposal. Where
these factors are present, recycling programs tend to be much more successful in both recovering material and
generating revenue.
Frequency: Many communities have resorted to bi- weekly recycling collection as a cost savings. Communities
attaining high recycling rates in the compared cities provide weekly collection. Weekly collection provides
residents with a simpler "everything out to the curb" model. Bi- weekly as an option in the interests of cost
savings must be balanced by providing adequate containers and reminders of the collection schedule to avoid
recyclables being disposed in the garbage because the resident "ran out of room" in the recycling bin.
4 Cost: Converting to a dual or single sort collection system requires some capital investment in equipment,
program modifications and public education. Changes in processing fees will be dependent upon the
arrangement with the MRF and the revenue sharing arrangement established with the City. These investment
factors are balanced against the increase in recycling resulting from a simpler method of setout and collection
for the community, and the savings realized from reduced waste disposal fees and collection costs.
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COLLECTION ASSESSMENT
LOCATION: ALLEY VS. CURBSIDE
Historically, refuse and recycling is set out and collected via the City's extensive alleyway system. Residents and
the collection team prefer the alleyways as it facilitates an easier set out and collection than a street side pickup.
Because the street is heavily utilized for parking, any additional space required for curbside pickup would prove
challenging and is not recommended.
WIDTH AND TURNING RADIUS
Eighty percent of the City's collection points are located in "` ' ,, ;, ' .,
alleys. Any new collection system will need to adapt to the °.
narrow characteristics and challenges found throughout ` '�� f.' `,, ,t' ' : °`
the city.
i
The average right -of -way in a Minneapolis alley is 12' with t
1 -2 ' of unpaved curb. There are areas where this is as .., . 1 -
narrow as 8.5'. In winter months, considerable amounts of r� � " 3 '
snow do accumulate on either side of the alley, effectively J ,. r ., :k +
narrowing the width even more. ; ' ;''''7-;' 1
i. 3 Routes also include a full range of traffic flows, from "T" '
- and "L" turns to dead -end alleyways that require backing a
vehicle into position. To complete the routes effectively and safely, RRS finds that only 96" wide chassis should
lk
be considered as well as trucks with at most a 27' turning radius.
''Al
HEIGHT RESTRICTIONS
The alleyways are also home to a network of ) ,.,:
x overhead utility wires that crisscross alleys at 12' to '
;; 14' high. Many carts are also placed under garage \ ,:
t overhangs with a similarly low 12' clearance. This fact,
coupled other obstructions, has lead RRS to • Iiir -- ',4'
I
recommend vehicles with a maximum riding height of -A r I
11'9 ". The height clearance restrictions also make _
other collection options difficult to operate if not , : 1 t,,,'.4
totally removing them from the realm of possibility.
OPTIONS 4„3.,., I,,,,, , '�
Considering the constraints of maneuverability, cart
placement, general conditions and available technology RRS suggests narrowing the focus to 20 -23 cubic yards
per day (CYD) rear load packers and smaller semi automated side loaders.
Standard, fully automated side load systems lift carts well above the obstruction height and then tip the
contents into a hopper. This system requires considerable height clearance, proper cart placement, and a wide
enough road to allow the lifter arm to operate. With current available technology, this option isn't viable.
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Semi- automated side load systems require a worker to
hook a recycling cart to a lifter arm that then •
mechanically dumps into the truck. This system is still -
a feasible option, but requires a proper height _ _
•
clearance that is problematic in many parts of the City.
•
•
The more traditional type of refuse /recycling truck - .i
setup is the rear - loading packer. In this system a
worker rolls carts to the lifting mechanism at the rear 1 , �.
of the truck, and the contents are then mechanically i -
dumped into the truck. This option requires the least
amount of height and width clearance to operate and
works best of the options noted, in the alley system operating in Minneapolis.
Table 10: Recycling Collection Options (Bodies)
Crane Labri Labrie
Chassis Heil Lodal
Criteria Expert t Expert
With 40-60 Rea 50/50*
Leach Bo. 000 1 00 !.
Type Rear loader Rear loader Side Loader Side Loader Side Loader
Single /Dual Single Sort Dual Sort Single Sort Dual Sort Dual Sort
Cycle time (Seconds) Not
(Time per Stop) 20 15-17 20 20
Provided
Capacity (cubic Yards) 20 20 -25 22 17 -24 23
Price ** $152,000 $180,000 $161,700 $173,700 $230,000
Height Clearance 11.5'
Height Above Frame gg" 102" 102"
(Body)
*Includes chassis and bodies
** Cost does not include cart lift mechanism or other body modifications
Based on the assessment of the constraints posed by the collection of recyclables in alleys, discussions with the
City of Minneapolis staff and on discussion with truck vendors it was determined that rear load 20 cubic yard
capacity trucks with short turn radius was the only viable option for the collection of recycling materials.
PILOT COLLECTION PROGRAM
Minneapolis conducted two pilot programs, testing the effectiveness of dual -sort and single -sort collection. Both
pilot programs incorporated recycling carts and collecting on the bi- weekly schedule. The results from these
pilots programs show a significant increase in number of stops that can be served by a single route and the
quantity of recyclables collected per household. These increases yield a higher recycling rate for a community, q Y Y P Y g Y g Y, a
reduced number of routes, fewer trucks required for collection per household.
•
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Table 11: Pilot Performance Metrics
Increase in Increase in Avg.
Program
Stops Weight lbs. /HH /Yr.
Single Sort
High Performing
Neighborhood 34.6% 31.0% 592
Low Performing
Neighborhood 74.6% 77.0% 338
Dual Sort
Average Performing
Neighborhood 92.6% 28.8% 474
Current Multiple Sort for
Participating HH 405
Current Multiple Sort for
1 All Dwelling Units 343
a
St. Paul, MN Dual Sort
All Dwelling Units 477
Portland, OR - Single Sort 659
Currently the City of Minneapolis uses side load multi sort trucks to collect curbside recycling and is in the
process of reviewing options for single and dual sort collection. RRS explored the best options in collection
vehicles, evaluated key features, and broadly associated a price to the various selections, including automated,
semi - automated, and manual load trucks. The City of Minneapolis collection routes include obstacles and unique
considerations that limit the range of viable options.
FOCUS GROUP MEETINGS
Focus Group meetings were held in two quadrants in the City which are currently provided with traditional,
curb -sort recycling collection and one meeting in each of the areas of the city that experienced pilot programs of
alternative collection services: one section participated in dual -sort collection, then transitioned to a single -sort
'', I and one section participated in a single -sort collection. The meetings were held in the residents' neighborhoods,
in local Park recreation buildings' meeting rooms.
Ni t
The Groups were identified as Group A Northeast Quadrant, Multi -Sort Curbside Service
: Group B Southwest Quadrant, Multi -Sort Curbside Service
Seward, Pilot Program, Dual Sort then Single Sort
'' Willard Hay & ECCO, Pilot Program, Single Sort
a >
The Focus Group participants were invited to attend the meetings by random selection of telephone numbers
published in the city directory. Specific addresses and names of individuals were unknown. A telephone call
script was prepared to provide a standard format to invite residents to participate in the group meetings.
The groups were intentionally kept small, which provided the opportunity for neighbors to meet and share his or
AI her attitudes towards recycling, recycling habits and discuss the service that would best meet their expectations
and needs for recycling.
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The meetings followed an agreed upon format. A brief review outlined the reasons the City is evaluating
recycling collection options and the potential impacts of any changes, based upon other communities'
experiences. The possible options for increasing recycling in the city and collection options were presented.
Key questions were prepared as guidelines to enable a conversation style for the meetings.
MEETING PARTICIPANTS
All participants have been recycling for a number of years, some for decades. Participants were a mix of ages
and family circumstances, including retired, young family with infant, grandparents who provide daycare for
grandchildren.
Every person participated and offered insights, experiences and support of improving the recycling program.
Each group also, via individual comments and observations, expressed their appreciation for the city's efforts to
evaluate and improve services and was aware that the city would be evaluating any service changes in terms of
the final cost for service and equipment.
The participants in all the groups expressed an interest and commitment to recycling that stems, in part, from a
desire to improve the environment and an awareness of other sustainability and green initiatives. Though
everyone did identify themselves as recyclers, there was a range of recycling awareness and participation levels.
In the area served by the single sort pilot program, a resident did acknowledge that she is recycling more now
that the program has been simplified.
ATTITUDES TOWARDS PROGRAMS AND COMPARABLE EXPERIENCES
There was an almost even division of life -long Minneapolis residents and those who have lived in other
communities. However, everyone has visited relatives or friends in other communities and has hosted guests in
their homes. This allowed a productive discussion of comparisons to the acceptance and ability to recycle in
various programs.
In the areas that have the established multi -sort curbside service, the participants expressed a desire and
support making the program simpler. The discussion covered the issue of simplifying the program to encourage
all the residents to participate at greater levels.
In the areas that have the pilot programs, the participants preferred the single -sort to the dual sort program.
Both programs were preferred to going back to the multi -sort system. One resident in the single sort pilot area
acknowledged that she recycles much more now that the program has been made simpler. In both pilot
program areas, there is agreement that recycling participation and volumes have increased.
Those who have lived in other communities have experience participating in single -sort collection, though most
have also visited relatives or friends who have an alternative to the multi -sort recycling program. Those who
have experienced single sort recycling felt it was simpler to participate and did not see any negative issues. One
resident commented that visiting relatives and friends often aren't very helpful because they don't understand
the multi -sort program.
Two of the groups included duplex owners, in which the owners occupied one of the units and the second was
rented. One of the groups was the multi -sort service and the other was in the dual -sort to single -sort pilot area.
The duplex owners shared their experiences that renters are less inclined to recycle and their frustrations to
encourage participation by renters. These residents share the perspective that too many neighbors do not
participate or support recycling and have a keen desire to have the program improved to increase participation
and volumes collected.
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The duplex owner from the single -sort pilot area brought her tenant with her. This provided an opportunity to
hear different perspectives, although the renter's attendance was indicative of the commitment to recycling.
The discussion and suggestions from the duplex residents included:
• Less commitment to recycling, the connection to the community is not as strong, renters move and a
new renter must be informed about the program.
• Difficulty of the multi -sort system for tenants, multiple containers in a smaller space, outdoor container
storage space
• Not "required ". One duplex owner has written into the lease that the renter must participate in the
recycling program.
In terms of recycling setouts, only two have curbside collection. All the residents with alley collection do not
want collection to be switched to curbside. In some portions of the city, switching to curbside would pose a
hardship, where there are steps to the curb and street and limited space at the curb. In addition, parked cars,
traffic flow and the aesthetics were viewed as restrictive to changing the collection.
i
' RECYCLING CARTS AND BINS
Residents in the multi -sort service areas shared their experiences and the challenges of setting out multiple
expressed
c ontainers. Some even shared tips with each other to make setouts easier. A couple of the residents ex
�_�, P P P
V guilt about going to the grocery store and asking for additional paper bags to use in their recycling program. One
;.' • resident carries cloth bags for grocery shopping, yet needs to obtain paper bags to recycle. Most acknowledged
g g Y P P g Y g
E
„i that if they don't have a full bag for a particular item, they consider whether to save and store the bag for
<
another week or throw the items in the garbage.
h;
Both duplex residents and single - family home residents supported increasing the size of recycling containers.
For those in the pilot areas, the recycling cart was well received and viewed as a plus for the programs and one
resident even hoped she would not have to return her cart at the end of the pilot program. No one felt there
i
were space problems in storing the larger cart.
In all the areas, when discussing the recycling carts, there was discussion and support for offering size options
,.] for residents based on household size and recycling generated. This led to an observation that the waste cart
could also be reduced as recycling participation increases.
t',; RECYCLING AWARENESS AND EDUCATION
v.
Most of the residents were very aware of the recycling program, what is included and how to set out materials.
If there is doubt about an item, residents acknowledged they throw it in the garbage.
Very few seemed aware of the City's website or have accessed the information provided. The primary source of
information for the residents is the mailed flyer or brochure. Every resident was aware of the information on the
flyer and many indicated where the brochure is stored or posted in the home as a reference. One of the
• residents especially noted the quality of the graphics and the information presented. Several supported
Ni providing a laminated version that could be posted in the home. In the pilot areas with recycling carts, residents
• thought a laminated version could be placed on the cart.
There is general support for increased education, outreach and events to increase awareness of recycling in the
r`r community and to encourage participation. Some of the suggestions and discussion included hiring an educator
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or coordinator, providing programs in the schools to help develop life -long recycling habits, organizing a team of
volunteers who could make presentations in schools or to groups, organizing tours of recycling facilities.
SPECIAL PROGRAMS AND ADDITIONAL SERVICES
Questions concerning special collections or recycling programs were not a part of the planned discussion.
However, every group mentioned how much they appreciate and want to see continued collection of bulky
items, recycling of electronics and the household hazardous waste programs. Several residents were also
interested and would like yard waste or organics recycling collection added to the program to enhance the
recovery of materials in the community. Residents are very happy that milk cartons and other types of cartons
were added, it adds to the recycling program.
All the groups discussed and agreed that reaching the recycling rate goal in the city would most likely need to
include multi - family services. The residents recognized that providing or requiring that multi - family units with
recycling service would be a longer -range goal that needs study and consideration.
COMMENTS
Each group quickly became comfortable in discussing the programs. Following are comments made during the
Y 'sII�
discussions:
• Preference for single sort, weekly collection; every other week can be confusing.
• Containers equipped with lids were preferred, to reduce litter, weather degrading the materials and
animals getting at the recycling.
• The single sort system is easier to explain, especially for residents who have moved from other
communities that offer a simpler system. The simpler you make the program, the more participation
and amount of recycling will occur.
• Would prefer single sort to dual sort because would have to store additional recycling carts.
• Need more education about recycling and ways to be more environmentally responsible in general.
• • Would like to see more items added if possible (plastic bags, egg cartons, other plastics, pizza boxes).
• Enforce some sort of penalty for not recycling
• Renters pose special challenges, the recycling program has to be explained and renters have to be
encouraged to recycle.
• Giving some form of credit for recycling is nice, but not necessary. If the rebate for recycling were
eliminated, it would not change the desire to recycle.
• Suggested if a reward is provided for recycling, it should be based on giving a higher reward for those
who recycle more
• Provide any incentives that help encourage recycling, anything that works.
• Supports whatever it takes to reach the recycling goal established by the County.
• Love the recycling cart and don't want to return it when the pilot program ends.
• Have seen more participation in the neighborhood, sometimes thought no one else recycled on the
block when putting out materials before the pilot program started.
• Realize that recycling saves money for the city, this should be promoted to the residents, and explain
the payback to the residents. If tipping /disposal costs are reduced, the money saved is actually a savings
for residents.
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COLLECTION OPTIONS ANALYSIS AND COSTS
An analysis of the performance and costs associated with transforming the Minneapolis collection program from
a multi -sort to a dual or single sort system was developed to provide a comparative assessment of the different
approaches. Although fully automated systems were evaluated, given the constraints presented by collection in
alleys it was determined that semi automated rear load collection options would be presented in this report.
This method of collecting recyclable material is also consistent with the consideration of collecting yard wastes
and other residential and commercial organic wastes through cart based collection programs.
Assumptions were developed based on the analysis of programs in other cities that have dual and single sort
collection programs and on the pilot collection programs conducted by the City of Minneapolis. The three key
assumptions derived from this information are the participation rate, the number of stops per day that a
collection truck can achieve in a constrained alley environment, and the increase in the amount of material that
participants will recycle on an annual basis. Other related assumptions include the size of the cart and the
capacity of the collection vehicle.
Table 12: Program Assumptions
l is t r 1 : ( r
Ir k 3
Size of Cart (gals) 96 64 2 x 64 1x64 1x32
Number of Carts for City Only
Households 52,594 52,594 105,188 105,188
Participation Rate 84.5% 90.0% 90.0% 90.0% 90.0%
Lbs. /HH /Year (Participating HH) 405 600 600 500 500
Lbs. /HH /Stop 15.6 23.1 11.5 19.2 9.6
Stops per Day per Truck
(Avg. City Route) 318 676 676 609 609
ti Truck Capacity (Cubic Yards) 20 20 20 20 20
The relationship between participation rate and the quantity of material that is recycled is a difficult variable to
balance. Minneapolis is characterized by a fairly high average participation rate but a low quantity per
household. This is explained by two factors. First, there are low performing neighborhoods in terms of both
participation and the quantity of material. Second, although there are high performing neighborhoods the
quantity of material set out is very low in comparison to other cities. Although there is no data to statistically
determine what the variations are on a neighborhood -by- neighborhood basis it was evident in the focus groups
that even highly motivated residents did not recycle all the material that the city accepts, primarily due to the
difficulty of separating the materials into nine different collection sorts.
ti
The frequency of collection on a weekly or bi- weekly basis has a major impact on the costs for trucks and
staffing. The current recycling program operated by the City of Minneapolis with city staff consist of a biweekly
pickup serviced by small trucks with pup trailers. In effect, half the households receive service one week and the
other half receive service on the alternate week. These fourteen multi sort trucks are each operated by a single
employee. Converting the collection program to a semi automated rear load collection truck results in a similar
operation level as the waste collection system that is also a semi automated rear load operation.
This means that there would be two staff per truck in this new configuration for a bi- weekly collection program.
Given the nearly 200% increase in the number of pickups per day that a semi automated truck can achieve over
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the current multi -sort program the impact is that half the trucks are required while maintaining the same
staffing level. A change to a weekly collection program would require double the number of trucks and a
doubling of the staff required to collect all households on a weekly basis. The collection time for single sort is
less than dual sort and there is no need to come off route when one compartment fills before the other.
Table 13: City Only Collection Operating Costs
Current Single Sort Single Sort Dual Sort Dual Sort
Program Area Multi -sort Semi Auto Semi Auto Semi Auto Semi Auto
Baseline Biweekly Weekly Biweekly Weekly
Labor with Benefits $1,031,338 $1,098,333 $2,036,263 $1,232,323 $2,304,243
O &M $488,400 $293,200 $464,000 $324,600 $519,800
Education $0 $100,000 $100,000 $100,000 $100,000
Customer Service $174,537 $174,537 $174,537 $174,537 $174,537
Total Annual Cost $1,694,275 $1,666,070 $2,774,800 $1,831,460 $3,098,580
Percentage Cost Change -1.7% 63.8% 8.1% 82.9%
The costs for the weekly and bi- weekly collection program for dual and single sort were based on the current
labor cost structure and the cost for purchasing rear load semi automated trucks as currently operating in the
waste fleet with the same cart tipping system. The operating and maintenance costs were adjusted based on the
number of trucks. The total annual cost based on current City of Minneapolis accounting practice illustrates that
dual and single sort bi- weekly programs can be implemented with very small impacts on the current operating
costs for the City.
Capital Costs for the collection vehicles were based on the most recent truck purchase for rear load semi
automated trucks with dual tippers. Dual sort collection requires significant truck capital purchase of dual rear
load split body packers ($30,000 more than single rear load). Cart cost for single sort (1 per unit) is estimated at
$6,800,000. Cart cost for dual sort (2 per unit) is estimated at $10,500,000. The total costs for new trucks for a
City of Minneapolis single sort; bi- weekly collection program is $8,840,000.
Table 14: Projected Capital for Collection Program
Current Single Sort .., Single Sort . Dual Sort Dual Sort
tions Multi -sort Semi Au o. -e i Aut.` Se Auto,' S i Attto
Size of Cart (gals) 96 64 2 x 64 1x64 1x32
Number of Carts 105,226 105,226 210,452 210,452
Number of Trucks (includes extra) 16 8 15 9 17
Total Cart Cost $6,839,690 $6,839,690 $10,522,600 $9,470,340
Total Truck Cost $3,952,000 $1,976,000 $3,705,000 $2,475,000 $4,675,000
The projected potential recycling rate and the quantity collected increase substantially from the current
program in all scenarios for single and dual sort programs. The bi- weekly programs can be implemented with a
low cost impact if any and can achieve much higher recovery rates. A single sort system will increase material
quantity recovered by 60% and the Minneapolis recycling rate increases from 18% to 32% (based on case studies
= such as Ann Arbor and Portland). A dual sort system will increase material quantity recovered by 36% and the
Minneapolis recycling rate increases from 18% to 25% (based on case studies such as Ann Arbor and Portland).
Although the total program costs for both the single sort and dual sort bi- weekly programs are similar the cost
per ton is much lower then the current multi sort bi- weekly program.
A rte
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Table 15: Projected Collection Program Recovery and Metrics
Current Single Sort Single Sort Dual Sort Dual So
Options Multi -sort Semi Auto Semi Auto Semi Auto Semi Au_
Baseline Biweekly Weekly Biweekly
City Tons per Year 9,010 14,200 14,200 11,833 11,833
Total Tons per Year 18,026 28,411 28,411 23,676 23,676
Percent Recovery Curbside *
(Rec /MSW) 18.1% 31.9% 31.9% 25.2% 25.2%
Cost /HH City Collection $32.21 $31.68 $52.76 $34.82 $58.92
Cost /HH /Month City Collection $2.68 $2.64 $4.40 $2.90 $4.91
Cost /ton City Collection Only $188 $117 $195 $155 $262
* A Recovery Percentage of 35% is achieved with 650 lbs. /HH /Year
The final analysis includes the impact on the revenue and disposal costs on the overall program costs. The net
revenue decline for all the new collection scenarios is due to the projected increase in processing fees. These
increase in costs are offset by the cost savings from the reduction in disposal fees paid to the Hennepin Energy
Resource Company (HERC). Appendix 11 details the projected tonnage and net revenue.
„ Table 16: Projected Net Recycling Costs
s
Current Single Sort Single Sort Dual Sort Dual Sort
Options Multi -Sort Semi Auto Semi Auto Semi Auto Semi Auto
Baseline Biweekly Weekly Biweekly Weekly
t. ' City Collection ($1,694,275) ($1,666,070) ($2,774,800) ($1,831,460) ($3,098,580)
MRI Collection ($1,694,593) ($1,666,371) ($2,775,301) ($1,831,791) ($3,099,139)
Total Collection Cost ($3,388,868) ($3,332,441) ($5,550,101) ($3,663,251) ($6,197,719)
Material Revenue* $1,640,937 $1,280,504 $1,280,504 $1,067,087 $1,067,087
Net Recycling Costs including
Revenue ($1,747,931) ($2,051,937) ($4,269,597) ($2,596,164) ($5,130,633)
Value of MSW Diverted $847,231 $1,335,318 $1,335,318 $1,112,765 $1,112,765
Net City Recycling Costs
(Annual Cost MSW Diverted ($900,701) ($716,619) ($2,934,279) ($1,483,399) ($4,017,868)
*Assumes a Processing cost for SS /DS = $70.00 and a Current Processing Cost = $24.04
The Net Recycling Cost is the lowest for the Single Sort Semi Automated Bi- weekly collection program by
approximately 20% while achieving a 32% recycling rate. The Dual Sort Bi- weekly program has a net cost of
. approximately 56% higher then the current multi -sort program and achieves a 25% recovery rate. A ten percent
increase in the quantity of material collected in the dual sort program achieves a 28.5% recycling rate with a net
'' cost that is 28% higher then the current program.
RECYCLING INCENTIVE PROGRAMS
We are all familiar with the old adage one mans trash another mans treasure." New companies are trying to
change that They say your trash is your own treasure, because you're going to pay you for it The concept,
called Incentive Based Recycling, is to increase recycling rates by providing a direct financial incentive for people
to go through the trouble of sorting their garbage. Participating customers receive a 35, 64, or 96- gallon
container that has a barcode that identifies their home. As the truck collects the recycling it scans the barcode
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on the container and translates the value of the recycled items into a dollar amount - that can be redeemed
though shopping coupons at participating businesses. The two major programs are: Recyclebank and Rewards
for Recycling.
Participants use an online interface to choose which coupons suit them best, order the coupons and receive
them by mail. Alternatively participants can choose to donate their Recyclebank Dollars to charity. Recyclebank
serves both residential and retail customers. Many paper, plastic, metal and glass recyclables are collected and
the company supports a single sort recycling system that allows all types of recyclables to be deposited in one
single container. Home collection of e-waste is coming soon but in the meantime customers can send in cell
phones for recycling by printing a envelope label including stamp directly from the website.
Recyclebank trades the actions a customer makes that have a positive impact on your home by saving energy,
community by recycling and the environment by conserving natural resources for points that you can use for
rewards you choose. Those rewards come in a variety of options: Products, discounts and coupons from the
world's leading brands (think: Kashi, Footlocker, Dunkin Donuts), or by donating your points to support
environmental education in schools.
Because Recyclebank offers coupons and other economic incentives to recycle, the RecycleBank model is
$` particularly attractive to lower- income communities. By rewarding households with coupons for groceries or
services, RecycleBank is having a direct positive impact on family budgets. Therefore, recycling becomes
something households participate in for financial assistance, rather than altruistic reasons. This is not meant to
suggest that the only people participating in RecycleBank are those on the lower end of the income spectrum,
only that the incentives inherent in the RecycleBank model become increasingly attractive the lower on the
spectrum a household lays.
Rewards for Recycling was founded in late 2008 with the express intent to provide a better recycling affinity
program option for municipalities and waste haulers. The Recycle Bank program was closely studied and
evaluated, and R4R was designed to be uniquely different, addressing all of the challenges we found in the
alternate system. The R4R program founders identified multiple challenges in the alternate system, specifically
a lack of understanding of basic marketing and consumer behavior patterns.
Rewards for Recycling is a community based Recycling program. R4R partners with the municipality, the
residents, the community and the local businesses. Rewards for Recycling rewards frequency and loyalty for
building recycling as a household habit. The program is open and available to all members within the
community. Rewards for Recycling provides rewards to every household immediately upon start -up, and
E continues to provide smaller value rewards to all households regardless of recycling activity. This methodology
provides the opportunity to continuously convert non - recyclers by showing them the rewards of significantly
higher value that will be available to them as soon as they begin recycling.
Local Business participation is a key component of the Rewards for Recycling program. The R4R Program
features rewards that come from the businesses located within each community. Restaurants, Pharmacies, Dry -
cleaners, Oil Changes and other retail products and services. The majority of them are locally owned and
operated, and employ local people.
The revenue generated by these businesses stays home and supports the local economy. R4R gives each
business an opportunity to offer valuable savings to residents free of charge. These offers can drive traffic to
local business. In addition, Rewards for Recycling has multiple promotional options available for local businesses
that can get them exposure in Direct mail, E- newsletter marketing and even television.
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INCENTIVE SYSTEM PROS AND CONS
Demographics are probably the most important factor to look at when considering an incentive system
partnership. An incentive system model is particularly attractive to lower- income communities because it offers
coupons and other economic incentives to recycle. By rewarding households with coupons for groceries or
services, an incentive system is having a direct positive impact on family budgets. Therefore, recycling becomes
something households participate in for financial assistance, rather than altruistic reasons. The following is a
partial listing of the pros and cons of incentive systems.
Pros
• Incentive -based program rewards recycling participation and builds good recycling habits
• Public awareness and participation in recycling rises
• Substantial rise in material volumes
• Data on the effectiveness of existing and proposed waste collection routes and strategies is collected
• Opportunity to modernize or upgrade the waste collection and recycling infrastructure
Cons
• System rewards consumption, not waste reduction
• Program may be a poor fit in communities with already high recycling participation
• Success relies on the participation of national and local businesses and retailers
• Upgrade costs could be prohibitively expensive for communities and smaller haulers if not adequately
negotiated with Service Provider
• Program not cost effective in areas with low -cost disposal
PROCESSING OPTIONS
Choices pertaining to both sorting technologies and overall processing choices are predominantly driven by
curbside collection systems. Substantial improvement in processing capability and efficiency has been
experienced in the past 5 -10 years. Beyond the initial use of magnets to capture ferrous metals at an efficient
rate, and eddy currents to separate and capture aluminum from the sort, more sophisticated equipment and
reconfiguration of the sorting systems has resulted in higher recovery rates, greater throughput, and less
contamination to meet market standards.
The number of recyclable materials has increased as the ability of secondary and manufacturing industries to
convert post- consumer packaging into marketable products has grown. Subsequently, the market demand for
the greater variety and volume of materials has driven MRF's to seek equipment that enable them to efficiently
recover an increased array of post- consumer plastics and fiber. The processes must also be designed to increase
the volumes or tons per day, to justify the investment in such equipment or systems.
MRF's and equipment manufacturers, to remain competitive and derive the greatest value from the collected
material, continue to improve the ability of the sorting methodology and performance standards. Systems are
configured to provide screening of non - recyclable materials and contaminants from a particular recyclable
material to yield a higher value end -of -sort product. Optical sorting technologies have advanced to enable
2 Resource Recycling Magazine, October, 2009
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efficient and broader range of sorting plastics and fiber cartons that results in an increased variety of accepted
materials for recycling at a higher marketable value.
Residual rates are an indicator of the success of the sorting systems and the recycling collection program.
Residual rates in both dual sort and single sort sorting systems have declined over the years, as evidenced in the
Table below. Whether dual sort or single sort, the ability to recover everything that is recyclable or marketable
and to remove waste that cannot be recycled is a key factor in determining the type of recycling program
provided. It is also a key measurable in determining overall recycling program success or failure.
A study' conducted for the MPCA by Tim Goodman & Associates to examine the issue of single- stream and dual -
stream recycling, focusing specifically on the processing of collected materials and the marketing of those
materials to end - markets. A key finding of that study stated: "The amount of processing residuals (including
mixed, broken glass) generated at the single- stream facilities serving the Minneapolis /St. Paul metro area varies
significantly from approximately 2% of throughput up to 17% of throughput ".
FIGURE 3: MATERIAL RECOVERY FACILITY (MRF) RESIDUAL RATE*
17.0%
xY N d'!/
10.0%
7.0%
a' 4.0% 4.0%
2.5%
0.6%
; .t Old Single Toledo Cincinnati Portland Ann Arbor National St Paul Minneapolis
Stream (SS) (SS) (SS) (SS) Average (DS) (MS)
Programs (DS)
* SS - Single Sort, DS - Dual Sort, MS - Multi Sort
Quality control remains a critical element in MRF recovery. At various points in the recovery process, testing or
checking of the commodity destined for markets can result in increased value to the commodity. The
community can also play a role in helping to increase the value of materials collected. To ensure quality
. >: standards, communities can require contracted MRF's to report volumes and percentages of recovered
materials by type, including residue rates; set minimum standards of recovery and residue, and the volume
of materials sold as various grades in the recycling markets. The Goodman study recommended certification
process be applied to MRFs. MRFs should be required to report certain operational data for monitoring
purposes. This information should include at a minimum:
• Amounts and types of recyclables delivered to the facility;
• Amounts and composition of processing residuals;
3 Single- Stream and Dual- Stream Recycling: Comparative Impacts of Commingled Recyclables Processing, Prepared For the
Minnesota Pollution Control Agency Tim Goodman & Associates, January 20, 2006
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• Amounts and types of materials processed and marketed on an annual basis; and
• Amounts and types of materials downgraded or rejected by markets.
Residual rates at the MRF can also be improved by education. As recycling participation increases, it is important
to provide direct, simple and positive education about what can be recycled. Consistent, accessible, user - friendly
education about what can be recycled makes an impact on the participants' participation to place the materials
that are accepted in the recycling container. Even with the most efficient system for sorting materials, if an item
that is not included in the recycling program is incorrectly placed in a recycling bin, it must be treated as residual
at the MRF.
SECONDARY MARKETS
Manufacturing techniques using post- consumer materials also have kept pace with technology and knowledge
of the materials sorts. Mills have improved their equipment and systems to predict and adapt to a degree of
contamination and to capture contaminants to minimize damage to equipment and maintain quality product
standards.
.; End markets for even more materials, especially the #3 - #7 plastics, has provided opportunities for MRF's to
1 increase their list of accepted materials and collected volumes. In fact, the capabilities of both dual and single
sort collection programs to easily add materials types to their collection programs has led to the expansion of
recycling programs nationwide. Without these inherent flexibilities, the successful recycling of cartons, juice
boxes, textiles, boxboard, and exotic plastics ( #3 - #7) would not have grown as quickly over the last five to ten
years.
MARKETS AND REVENUE FOR MATERIALS
j All materials collected and ultimately processed in a recycling program are considered commodities. This means
that in spite of market demand fluctuations and associated price increases or decreases, the total collected
tonnages must yield a profit to maintain a healthy, stable recycling program. In reviewing the Market Trends
Data, the market demand and commodity prices for fiber, plastics, aluminum and steel have remained strong to
1 ?; stable. Two brief periods in the early 1990's and mid 2000's have seen brief price tumbles. But recycled
commodity price rebounds have been quick and over time have shown an almost universal strengthening. The
commodity revenues associated with these materials have over time provided the financial foundation for most
recycling programs, whether publicly or privately sponsored.
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FIGURE 4: MARKET TREND DATA
Average Price for Curbside Recycled Materials
Pacific Northwest, 1985 -2011
$180 —
9160 —
$140 —
$120 —
$100
0
$80 —
S88
$60 —
$40 — $64
550
$20 533
as 86 87 88 89 90 91 92 93 94 95 96 97 98 99 00 01 02 03 04 OS 06 07 08 09 10 11 12
Communities can choose to request MRF's to share in the market value of materials that are sold, as contracts
are prepared. This is a typical practice when separate contracts are awarded for collection and for processing
and marketing of materials. A revenue sharing arrangement provides an incentive for both the MRF to maintain
high quality and market standards and for the community to encourage residents to participate in the recycling
4LL' program and educate residents how materials should be set out to maximize the benefit of the program.
> y= A market share arrangement generally includes an established floor price, which guarantees a minimum price
per ton paid to the community for materials brought to the MRF. The floor price can be fixed based on the
market value of a select number of items or the total mix of recyclable materials collected. When the market
value of the recyclable tonnages exceeds the established floor price, the community and the MRF share in the
value of the sold commodities, based upon an established percentage split.
As an example: Cincinnati has a market share arrangement with their MRF, operated by Rumpke, which provides
a floor price of $85 /ton. If the revenue from sale of the materials exceeds $85 /ton, 50% of the revenue above
$85 /ton is shared with the city.
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GENERAL DISCUSSION OF DUAL -SORT RECYCLING
Background on Dual -Sort
Dual -sort recycling is a collection and processing system where mixed bottles and cans are collected in one
compartment and mixed fiber is collected in another compartment. For many years and until recently, this
technology has been the default choice for large -scale residential recycling operations in the US.
As more programs recognized the high cost of paying drivers to sort material at the curb, efforts focused on
finding a collection method that did not require sorting at the curb. Programs found that residents responded
well to being asked to sort materials into two containers. These two containers could be dumped into the
collection vehicles with no curb -sort. By 1990, most new recycling facilities were being designed with dual -sort
sorting capabilities.
The reduced cost of dual -sort curbside collection was traded off against the increased cost of central sorting. An
incentive for doing this was the increased ability to accept a wider range of recyclable materials and still produce
marketable products from the collected materials. Many dual -sort facilities were designed with the ability to
sort to more than 20 products. A typical dual -sort program collects and processes at least the following list of
materials:
• Fiber sort
o Newspaper
o Cardboard
o Paper bags (depending on local markets this might be baled with cardboard)
o Magazines (depending on local markets this might be baled with news or mixed paper)
o Junk mail (depending on local markets this might be baled with news or mixed paper)
o Boxboard (depending on local markets this might be baled with news or mixed paper)
• Container sort
o Clear glass
o Colored glass (Green & Brown) (in many areas, glass is no longer color sorted at the MRF)
o Steel cans
o Aluminum cans
o Natural HDPE plastic bottles
o Colored HDPE bottles
o PET bottles
A number of dual -sort programs have also added the following materials:
• Fiber sort
o Shredded paper (depending on local markets this might be baled with SOP or mixed paper)
o White office paper (SWL) (depending on local markets this might be baled with SOP)
o Mixed office paper (SOP)
• Container sort
o Colored PET bottles (only common in a few regions)
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o Mixed plastic containers (small food tubs, clamshells, trays, etc.)
o Large rigid plastics (lawn furniture, buckets, large plastic toys)
o Cartons (aseptic and milk & juice gable -top)
o Junk metal (some restrictions on size and material need to apply)
o Plastic film (plastic bags, and stretch & shrink wrap)
The junk metals, plastic film and large rigid plastics are challenging to handle in a cost effective manner, so these
materials are often directed to a drop -off collection that compliments curbside collection.
Dual - Sort Scale of Operations
Dual -sort systems have been built to operate in sizes ranging from less than 2,500 tons per year (tpy) to over
200,000 tpy. In smaller facilities, nearly all sorting is done manually. Many of these smaller facilities have only
one sorting line that is used alternately for containers and fiber. Larger facilities that require more throughputs
have specialized sorting lines that utilize staff more efficiently. Larger facilities also add mechanical separation
technologies such as
• Cardboard (OCC) screen to separate large cardboard from other fiber
• Magnet to remove steel cans from other bottles and cans
• Fines Removal Screen or Glass Breaker to remove broken glass and dirt from bottles and cans
• Density Separator to remove glass from lighter bottles and cans (if no glass breaker)
• Eddy Current Separator (ECS) to separate aluminum from other containers
• Optical Sort to sort plastics by resin type or to sort other optically identifiable materials such as cartons
Dual - Sort Sequence of Operation
A typical single sort processing facility has two sort lines and one or more balers. Eureka Recycling is an example
of a medium -large dual -sort processing facility. See Appendix III for s diagram of a Dual Sort Process Flow
Diagram. A Dual Sort facility consists of the following processing sequences.
Fiber Sort Line:
• Mixed fiber is dumped from the collection vehicle onto the tipping floor
• A large loader pushes materials up and then loads them onto an in -floor metering conveyor as
sorting progresses
• An inclined conveyor carries mixed fiber up to the pre -sort conveyor where sorting staff removes
trash and oversized items
• Cleaned fiber falls onto the cardboard (OCC) screen. Smaller fiber passes through the screen and
OCC is conveyed off the end of the screen and piled on the floor where a loader can later load
sorted OCC onto the baler feed conveyor.
• Smaller fiber is conveyed to the main sort conveyor where staff picks off small OCC, trash and other
5 •'' products. Cleaned newspaper (ONP) drops off the end of the sort conveyor onto a conveyor that
feeds to a baler.
Container Sort Line:
*;fi
• Containers are dumped from the collection vehicle onto the tipping floor
• A large loader pushes materials up and then loads them onto an in -floor metering conveyor as
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• An inclined conveyor carries mixed fiber up to the pre -sort conveyor where sorting staff removes
fiber products, trash, and oversized items
• Material passes under an overhead self - cleaning magnet that removes steel (includes tin plated)
cans and other ferrous metal to a conveyor that leads to a storage bin
• The rest of the bottles and cans pass over a roll- screen that drops out small glass, dirt, and other
fines
• The overs are fed to a density separator that pulls the plastics, aluminum and cartons (if present)
separate from the remaining glass. The glass continues to a manual glass sort line where the glass
can be manually color sorted
• Aluminum is sorted from the light fraction using and Eddy Current Separator (ECS). The aluminum is
conveyed to a storage bin by a blower /duct system.
• The remaining light fraction is conveyed to an elevated sort line where staff sorts remaining plastics
and cartons
GENERAL DISCUSSION OF SINGLE -SORT RECYCLING
Background on Single -Sort
Single -sort recycling is a collection and processing system where all bottles and cans are combined with all fiber
i
in one collection container. This technology has been a significant part of residential recycling in the US for
approximately 10 years. The technology for single -sort processing is still evolving rapidly. The appeal of single-
,.:.
sort recycling comes from several factors:
• Residents place all recyclables in one container. This is often a cart with a lid that can be stored
outside without other cover. In most communities this makes recycling easier for residents and
provides residents with more recycling container capacity
• Most single -sort rollouts have resulted in significant increases in recycling collection volumes. In
many areas where Recycle Bank or other incentive programs have been included, the increases have
been dramatic.
• Adding new materials is very easy for residents because they just add the material to the one
container. There is no confusion in what bin to place a new recyclable.
4 • Collection costs are usually less than for other curbside recycling technologies. This is true whether
the driver must dump tubs, dump carts with a mechanical cart dumper or if the driver can sit in the
cab and dump carts with an automated robotic arm. Because there is only one container, each stop
takes less time than dumping the same container type with multiple containers. Less time at a stop
means a driver can pick up at more stops in a day.
• Automated cart dumping usually results in significant reduction of workers compensation claims,
since most carts can be dumped without manual handling.
• When using automated collection vehicles, identical collection vehicles can often be used for
recyclables, organics and trash. Having all the same vehicle requirements simplifies fleet service and
parts inventory and allows rededication of trucks with just a change in signage or paint.
• The collection vehicle needs only one compartment for recyclables, which means compaction is
s 3S common and usually more stops can be made before returning to empty.
.;c. } • Multiple compartment trucks can collect trash and organic waste with recyclables where a single
tqr provider offers two or three services. Combined collection reduces truck traffic on any one street
and reduces total fuel consumption where alternate week service is not acceptable.
• Collected recyclables can be hauled long distances cost effectively. All recyclables can be tipped in
one pile and loaded into a single transfer trailer. This allows a single processing facility to
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competitively serve residents in large radius (in some cases over 200 miles). Hub and spoke regional
recycling service is becoming practical in many underserved parts of the US as a result of simplified
transfer.
• Except for color sorted glass and plastic film, recent large single -sort facilities are able to efficiently
sort recyclables and produce quality products with comparable or less labor cost than in a similarly
sized dual -sort facility.
• Many recent single -sort facilities incorporate secondary fiber recovery and other scavenging
technologies are able to achieve residue rates approaching that of dual -sort facilities
Early Single - Sort Problems
Early single -sort processing facilities exhibited some problems. The two most significant problems are
described below:
• The most cited problem is high residue rates. High residue rates were common in early facilities.
These high rates resulted from a combination of unrefined processing technologies, loss of driver
quality control and poor education of residents. Because fiber and containers are mixed, reclaiming
small recyclables from residuals is more complex than for the same target materials in dual- sort
facilities. Shredded paper, fine glass, plastic film and caps and lids are among the most challenging
materials to recover. Newer facilities that are designed with the capability to reduce residue and
with an operator that committed low residue can achieve low residue rates.
• The other common problem for early single -sort facilities was poor product quality. The main
product quality issues have been with glass and lids in fiber products and glass in plastic products.
,'. Also, early screens were not able to separate newspaper from other paper grades very well. Newer
separation screens can produce products that compete with the best dual sort product quality.
Newer screen especially when combined with a glass breaker at the front end of the system are able
to produce products rivaling that of dual -sort facilities
Challenges
' Single -sort recycling does not solve all problems for recyclers. A number of challenges remain for a single -sort
facility operator.
• Single -sort processing equipment is more sensitive to certain materials than most dual -sort
processing lines. In particular, plastic film, garden hoses, rope, cords, wire, strapping and chains
quickly become wrapped around screen shafts. Allowing these materials to reach the separation
q Y PP g P
screens can result and reduced screen efficiency, lost production time and in some cases, the need
for costly repairs.
• Most single -sort facilities often operate at a higher residual rate than comparably sized dual -sort
facilities. With good education of residents, sufficient pre -sort effort, modern reclaim features and
manual reclaim from the residual sort, residuals of less than five percent are common. Lower rates
are possible with additional picking staff and management committed to low residuals. This extra
effort can in some cases increase operating cost.
• Single -sort processing equipment is more costly to purchase than that of a comparably sized dual-
sort facility. This is especially true for smaller facilities where single -sort equipment does not scale
well. When significant quantities of mechanized sorting are added to a dual -sort facility, the capital
cost of the dual -sort facility may approach that of the single -sort facility.
• Single -sort facilities require more maintenance and more expensive maintenance than dual -sort
facilities. More equipment needs maintenance, but also, a higher level of skill is needed to perform
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some of the maintenance. Hundreds of screen discs must be changed every 12 -24 months and
these typically cost $40 each.
Improved Technologies
Most recent single -sort processing facilities incorporate a number of improved technologies that improve
operating efficiency, product quality and reduce residue as compared to earlier facilities. While these add to the
facility capital cost, an acceptable return on investment can be demonstrated when the features are applied
appropriately. A partial list of improvements follows:
• Front end metering to keep the flow of materials very close to the optimum capability of the line for
the mix being fed and to simplify line loading and allow loader operator to perform other tasks.
• Large presort to remove trash, oversize materials and materials that might wrap on screen shafts,
and to allow recycling of large rigid plastics and scrap metals
• News and Mixed Paper screens have been much improved, reducing the amount of post sort
needed to produce marketable products, and at the same time providing a cleaner sort to the
container line.
• Where significant volumes of cardboard are present sort, adding an OCC screen at front end to
eliminate most manual sorting of OCC. This makes other screens more effective and reduces
staffing requirements at presort and at fiber post sorts.
• Glass removal at front end to get glass out of other products and to prolong the life of equipment.
• Glass cleanup systems to improve glass quality and in some facilities to reclaim small (shredded)
fiber for recycling
• Fiber reclaim from mixed container sort to reduce residue and recycle more fiber
• Bottle and can reclaim conveyors from fiber post sort lines
• Optical plastic sorting to reduce labor needs, increase throughput and efficiency and sort grades
that humans cannot differentiate visually (ex: PLA vs. PET). Optical sorting can be used for PET,
7,1
NHDPE, colored HDPE, PLA, #3 -7 (or grades within), aseptic cartons, milk and juice cartons and
various combinations of these. Optical sorters can also be used to color sorts where the markets
demand this effort (ex: green PET or light and dark CHDPE). The quality of sort and reliability of this
equipment has improved dramatically in recent years. Also, dual -sort optical sorters perform well in
some applications to sort two products from the sort at one time
While most of the above technologies can be applied to dual -sort systems, most dual -sort MRFs are not
operating at a scale to justify these solutions. Single -sort programs are capable of collecting all of the materials
that can be collected in dual -sort systems. The list of materials in the Dual -Sort discussion above also applies
here.
Because some materials will clog or jam the mechanical sorting equipment, additional efforts may be needed at
the pre -sort to remove these materials. Examples of materials that generally need to be removed at pre -sort
include large rigid plastic, junk metal and plastic film. These materials are manually sorted from the sort at the
pre -sort station. This can be costly for plastic film where a good deal of hand motion is required to sort just one
pound of material. Missed plastic film wraps on the screen shafts and must be cut off frequently. These
materials that cannot be easily sorted mechanically are often directed to drop -off collections that take these
materials and other difficult to handle recyclables.
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Single -Sort Scale of Operation
Historically the throughput sweet spot for single -sort facilities has been 15 ton per hour (tph) or 30,000 tons per
year (tpy) or greater. This was based on the early screens that separated fiber from containers performing well
at 15 tons per hour. The screens could be run at lower rates, but manual sorting staff requirements did not
decrease much because of the sort locations that must be staffed, making smaller facilities proportionately
more costly to operate. Some facilities were built in the 8 tph size range, using smaller or less advanced screen
designs, mostly to serve isolated populations, large rural areas or where recycling rates are low. These lower
throughput facilities could not compete economically with larger facilities where sufficient volume of recyclables
is available.
Recent designs with a single sort line appear to perform well in the 15 -35 tph -size ranges. At throughputs below
35 tph, increased capacity is obtained through increase in size of separation equipment and increase in the
number of separation stages rather than through parallel equipment. The primary advantage of this approach is
that little additional staff is required to increase throughput. As a bonus, the additional separation stages also
' have the potential of providing better separation quality and automated production of additional fiber grades.
? Most equipment designers choose to split the material sort after the OCC screen into two lines when processing
35 tph or more rather than build huge components to handle it all as one sort. This allows for a
I loading /metering station, a single large presort and a single OCC screen. These split systems have been
1 designed to operate at more than 50 tons per hour. Usually, containers are recombined into a single sort for
optical sorting.
i
I Facilities sized to process 50,000 tons or more per year usually justify optical sorters for PET and NHDPE. A
number of facilities in this size range are also adding optical sort for CHDPE, #3 -7 plastics and cartons. Many
larger facilities add more optical and mechanical sorting rather than increasing staff.
1
A number of facilities have been built to process more than 200,000 tons per year Most recent large facilities
efe
e l
use optical sorters for most plastics. A few MRFs use optical sorters to post sort mixed fiber. These larger
facilities are usually set up to receive transfer trailers and to serve a large geographical area In the Chicago
area several large MRFs compete, drawing materials from five to seven states.
e ;t
Sequence of Operation
' The separation technologies vary somewhat from one manufacturer to another, but with a few exceptions there
0, 1 1 ` i s general agreement process eneral a reement on the se The two areas where design sequences significantly are the
0 sequence. g q uences var Y g Y
' ` " " place and method of glass removal and the place and method of small fiber recovery. See Appendix IV for a
4 d,
, diagram of the Single Sort Process Flow Diagram. The following describes a typical single -sort equipment
o;, sequence:
il
`` Lo adin hopper— is usual) loaded from the ti in floor b a lar a wheel loader
�� Loading pp Y pp� g Y g
( • Metering (either metering drum from hopper or metering drum over inclined conveyor following hopper
: with optical feedback control)
• Presort — A large horizontal conveyor with picking stations for materials such as trash, large rigid plastic,
junk metal, any materials that might wrap screen shafts. If no OCC screen follows, large OCC is
:, 1 Y g p picked
g p
I l i here. If plastic film is collected, overhead suction tubes may be provided for film collection from sorters'
a r ;
hands.
, OCC screen — Large OCC is removed (not needed in facilities where little OCC shows up in single -sort in-
:
I feed)
C .a
Most facilities provide a an OCC post -sort station that may or may not be staffed
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Crty of takes
• Second presort — Needed where lots of large OCC is delivered in single -sort materials because it is
difficult to see under the large OCC
• Glass removal —This can be done under OCC screen (BHS) or under a scalping screen following OCC
screen (CP). This is often accomplished with a multi -stage all -metal roll- screen designed to break and
screen glass from other materials. Glass is usually directed to a glass clean up system to remove most
non -glass materials before the glass is stacked in a bunker.
• The materials that pass through the OCC screen but not the glass breaker are fed to a news screen that
separates newspaper from bottles and cans with smaller fiber. The ONP goes to a post sort station
where brown paper /OCC, contaminants and out -throw are sorted to achieve the required market
specification.
• The bottles and cans with smaller fiber (unders) from the news screen pass to the next screen which
separates mixed paper from the mixed bottles and cans. The mixed paper goes to a post sort station
where bottles and cans, contaminants and newspaper that was not captures by the news screen are
manually sorted to appropriate bins or conveyors.
• The small paper that comes out with the bottles and cans from the mixed paper screen is recaptured
either as part of the mixed paper screen operation or as a secondary process (CP uses air drum
separators — ADS). Small paper is fed to the mixed paper post sort.
• The bottles and cans are conveyed to the container sort section. Steel cans are pulled off with an
overhead magnet.
• Optical sorters remove PET, NHDPE and possibly other materials (CHDPE, #3 -7, cartons). Post sort
manual inspection stations allow sorting materials missed by optical sorters. If PETG must be kept
separate from PETE, this is usually accomplished manually at the PET post sort station.
• Materials not sorted by optical sorters are manually sorted into appropriate bins
• If aluminum is left on the line, an eddy current separator (ECS) captures the aluminum. Post sort stations
can be staffed to capture missed aluminum and pick recyclables from residue. Some facilities manually
sort foil items such as pie tins, but leave cans on conveyor for ECS, either to bale these materials
separately or because some ECS units do not sort foil well.
• Manual residuals sorting of recyclables missed on line. This position is built in most new facilities, but
}
often not staffed.
• All sorted materials are stored in bunkers and bins and fed to one or more balers as bins fill.
1
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ADDING MATERIALS TO THE RECYCLING SORT
A number of MRFs recycle several materials that Minneapolis does not yet accept.
• Metal recycling could also be expanded.
• Minneapolis does collect most fiber materials. Depending on local markets, Minneapolis may be
able to recycle other poly- coated papers with cartons or as a separate fiber grade
• While markets for post consumer plastics other than #1 (PET) and #2 (HDPE) bottles have not yet
matured, Minneapolis could substantially increase plastic recycling. Most processors are having no
problem marketing the plastics they receive as long as the material is clean. The three most
common inputs are plastic film and large rigid plastics.
Each of these possible new materials is discussed in some detail in the following sections.
METALS
Many curbside collection programs include junk metals. In dual -sort recycling these materials are collected with
containers and pulled out at the pre -sort station. In single -sort recycling the junk metals are pulled out at the
main pre -sort station. The challenge with junk metals is defining what is and is not accepted and making sure
residents are aware of the acceptable limits. In order for the collected material, to have good value to the
; 4 recycler, it needs to be clear that toaster ovens and microwaves are not accepted because a large portion of
1 them is not metal. Usually automobile parts are excluded, but items such as pots and pans are encouraged. ER
'_. could add junk metals if in expanding its container pre -sort a chutes and a bunker are added for this material. If
ER moves to single -sort collection, similarly, a place for this material could be included in the pre -sort. Amounts
collected vary widely depending on restriction on materials and other entities that accept metals in the area
RRS Recommends that ER consider recycling junk metals.
POLY - COATED FIBER
Poly- coated fiber is used to package many refrigerated and frozen food products as well as used for
manufacture of paper cups. Some packages are coated on one side only while others are coated on both sides.
Single coated packages may have printing on the fiber, where as on double coated fiber, the ink is usually on the
poly. These packages also contain varying amounts of wet strength resin in the fiber. Accordingly, not all mills
4
that accept cartons can accept these materials. Where these materials can be sold with the cartons, the volume
of poly- coated fiber can typically be doubled over the volume of cartons (aseptic plus gable -top) alone. Poly
4
coated packaging presents a challenge for collection and separation. In dual -sort collection, it is usually
collected with containers. This can be confusing to residents. In single -sort processing, flattened packages may
be mechanically sorted to mixed paper, while 3 -D packages will be sorted to containers. Optical sorters can
readily identify /sort poly- coated fiber on the container line, but manual sorting would be required to pull this
° �mo t material from the mixed paper. RRS recommends that ER explore marketing opportunities for this material. If a
range of poly- coated fiber can be mixed with cartons and sold at the same price, RRS recommends that ER
,i
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I t, explore feasibility adding existing Y ex lore the feasibilit of addin this material. In the existin system, no new hardware would be needed.
PLASTIC FILM
Plastic film can include plastic shopping and produce bags, industrial shrink -wrap, industrial stretch wrap and a
variety of other bags and wraps. Plastic films of low- density polyethylene (LDPE), medium density polyethylene
`, (MDPE), high- density polyethylene and polypropylene are common. All of these plastics belong to the polyolefin
z family. Most industrial shrink and stretch wraps are also polyolefin. Most MRFs that receive plastic film bale it
-`- City of Minneapolis: Dual Sort /Single Sort Collection Study May 10, 2012
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Resource Recycling Systems
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Sustainable Systems fora Waste Free Future 5 E H
Minneapolis
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all together. Mixed polyolefin is used in making plastic lumber and other products that do not require specific
melt and flow properties. If specific resins can be baled separately, the plastic film has a much higher value and
the plastic be recycled into higher end products.
In areas where a large number of boats are shrink - wrapped for winter storage, having a bunker designated to
stockpile this material every spring can be profitable. Distribution centers that restack pallets are often a
significant year -round source of natural colored shrink and stretch wrap. If ER can encourage haulers to bring
post- industrial clean plastic film to the MRF, ER can make money baling and selling this product. The price for
clean post - industrial wrap varies, but $200- 300 /ton is common in some areas.
Residential plastic film is primarily plastic bags. Most grocery shopping bags are HDPE and most produce and
bread bags are LDPE, however, there is no standard. Most manufacturers of recycled content bags need
=r4 material sorted by resin type. Plastic film is difficult to sort manually, mechanically or optically, so making
' shopping bags from shopping bags is not generally cost effective. The biggest problem in collection is making
sure that bags are clean. Significant food contamination is a problem for nearly all buyers.
' If plastic film is collected curbside, some means of consolidation is needed to keep bags from blowing around
t and to allow efficient sorting at the MRF. One of the most effective methods thus far observed is known as
i
"Bag- the - Bag ". In this approach, residents are instructed to stuff all bags in one outer bag and to tie the outer
bag shut when the bag is full. The full bag is then placed at the curb with other recyclables.
If collecting dual -sort, residents can be instructed to place the bag with either containers or fiber. Fiber is
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usually the preferred option, because bags can be sorted to a bunker either at pre -sort or at the main sort. If
included with containers, bags must be picked at the pre -sort and the likelihood of contamination with broken
glass is much higher. If collected in a single -sort program, bags must be picked at the pre -sort. Overhead
suction tubes are often used to convey bags from multiple pick points to a common bunker. Because it takes
from 200,000 to over 1,000,000 bags to make a bale, picking individual bags is not practical unless labor cost is
very low. As a percentage of the total recycling sort, plastic bags are a small percentage. In programs
aggressively collecting plastic bas, they can make up as much as 0.5% of the recycling - gg Y g P g Y p Y g sort. The value of this
,,
} material varies wildly from $40- 200 /ton depending on product quality and available markets.
Based on programs that have been observed thus far, RRS does not recommend that ER collect bags curbside.
The challenge is getting residents to keep bags clean and consolidate them for efficient sorting. While residents
are generally eager to add bags to their recycling, this can be a costly addition to the bin without ascertaining
that residents will prepare the bags properly.
LARGE RIGID PLASTICS
Large Rigid Plastic usually refers to a wide variety of large molded objects. Lawn furniture, riding toys, play
structures, buckets, large tubs, and a number of other larger molded plastic objects are typically included. The
F, objects are mostly made from HDPE and PP. Because the pieces are large, hand sorting at secondary processor
into specific resins is even practical in the US, though much of this material is sold off shore. This material is
easily collected at drop -off stations, and is collected in many curbside programs. When collected single -sort this
$4 material is pulled out manually at the pre -sort. In dual -sort collection, this material is almost always collected in
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the container sort.
The primary problem with large rigid plastics is the physical size of the object. Some programs limit the size of
the largest piece. Others require that all objects fit in the collection bin or cart. Collection works best if the
truck can compact the object, to avoid having the compartment on the truck fill prematurely.
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