Solid Waste Characterization Study Final Report - 1997
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City of Salina
Solid Waste Characterization Study
Final Report
August 1997
Prepared for:
City of Salina, Kansas
Prepared by:
Camp Dresser & McKee Inc.
555 N. Woodlawn, Bldg 1, Suite 215
Wichita, Kansas 67208
CDM Project No: 8558-20193
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Table of Contents
EXECUTIVE SUMMARY
1.0 INTRODUCTION ................................................ . . . . . .. 1-1
2.0 STUDY APPROACH .................................................... 2-1
2.1 Introduction .......................................................... 2-1
2.2 Waste Audit . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-1
2.2.1 Landfilled Waste . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-1
2.2.2 Construction and Demolition (CID) Waste. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-5
2.2.3 Recycled Materials ................................................ 2-5
2.3 Sampling Event W orkplan . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-7
3.0 LANDFILLED WASTE COMPOSITION FINDINGS. . . . . . . . . . . . . . . . . . . . . . . . . 3-1
3.1 Introduction .......................................................... 3-1
3.2 "Landfilled" Material Waste Streams ...................................... 3-1
3.2.1 Residential Waste Stream . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-1
3.2.2 Commercial Waste Stream. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .'. '. . . 3-1
3.2.3 Industrial Waste Stream ............................................ 3-3
3.2.4 ConstructionlDemolition Waste Stream. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-3
3.2.5 Combined "Landfilled" Wastes .................:.................... 3-7
4.0 TOTAL WASTE STREAM COMPOSITION FINDINGS...................... 4-1
4.1 "Non-Landfilled" Material Waste Streams .................................. 4-1
4.1.1 Recycled Waste Stream ............................................ 4-1
4.1.2 "Other" CID Waste Stream . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-1
4.2 Combined Total Generated Wastes. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-3
5.0 CONCLUSIONS AND RECOMMENDATIONS ..............................5-1
5.1 Conclusions .......................................................... 5-1
5.2 Recommendations. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-4
APPENDIX- A - CITY OF SALINA SOLID WASTE CHARACTERIZA nON WORKPLAN
APPENDIX B -SAMPLING EVENT WASTE CHARACTERIZATION RESULTS
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List of Tables
2-1 Interviewed Waste Generators, Handlers, and Recyclers
2-2 Saline County Hauling Companies
2-3 Current Handling Methods for C&D Materials in Saline County
2-4 Current Annual Tonnages of Recyclable Materials in Saline County
3-1 Annual Landfilled Quantities By Material Type
3-2 Statistical Analysis of Landfilled Waste Stream
4-1 Fall Quarter Tonnages of "Other" C&D Materials
4-2 Composition of Combined Total Generated Waste by Weight
5-1 Current Recycling Levels of the Residential and Commercial Waste Streams
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List of Figures
2-1 Collection Routes of Saline County Haulers
3-1 Composition of Residential Waste Stream By Weight
3-2 Composition of Commercial Waste Stream By Weight
3-3 Composition of Industrial Waste Stream By Weight
3-4 Composition of Construction/Demolition Waste Stream By Weight
3-5 Composition of Combined Landfilled Waste Streams by Weight
4-1 Distribution of Materials in the Recycled Waste Stream By Weight
4-2 Composition of Total Waste Stream by Weight
5-1 Potential Recyclable Materialin Saline County
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Executive Summary
The City of Salina and Saline County contracted Camp Dresser & McKee Inc. (CDM), under a
Kansas Department of Health and Environment (KDHE) grant, to assess the characteristics of
the solid waste generated in Saline County and, in particular, the characteristics of the solid
waste disposed in the City of Salina Municipal Solid Waste Landfill (MSWLF). The purpose of
the study is to develop an understanding of the types of materials that comprise the solid waste
stream of Saline County. With this knowledge, the City and County can better establish
program goals to maximize the ec.onomic efficiency of the solid waste handling systems.
This characterization study was conducted over three seasons. This final report details the
results of the three sampling events conducted during the fall, winter and spring/summer.
Items of significance for the landfilled waste stream (disposed in the City of Salina MSWLF)
include:
. Residential waste accounts for 32.3% (by weight) of the totallandfilled waste. .
Leaves/ other yard waste is the largest annual component (15.1 %) of the landfilled
residential waste stream with other paper being second (12.3%).
. Commercial waste accounts for 21.4% (by weight) of the totallandfilled waste.
Corrugated & kraft paper is the largest component (18.1 %) of the landfilled commercial
waste stream with food wastes being second (14.4%).
. Industrial waste accounts for 27.3% (by weight) of the total land filled waste. The largest
components of the landfilled industrial waste stream include glass from Philip's Lighting
(33%) and food waste from Tony's Pizza (29%).
. Construction/ demolition waste accounts for 12.2% (by weight) of the totallandfilled
waste. Roofing material is the largest component (36.1 %) of this waste stream with clean
wood being second (27.8%).
. Food waste (14.7%), corrugated & kraft paper (13.4%), other paper (8.6%), and glass
(7.6%) are the largest components (by weight) in the combined landfilled waste stream.
This is exclusive of concrete and asphalt.
CDM Camp Dresser & McKee
ES-1
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Estimated Annual Quantities of the Landfilled Waste Stream
City of Salina MSWLF
I I Annual hshmated Tonnages I Annual hshmatedMean I
. Food Waste 10,414 14.7%
Corrugated & Kraft Paper 9,312 13.4%
Other Paper 5,924 8.6%
Other Glass 5,550 7.6%
Clean Wood 5,508 7.4%
Leaves/ Other Yard Waste 5,711 7.5%
Roofinf!: Materials 4037 5.0%
Items of significance for the total waste stream generated in Saline County include:
. Ferrous metal (6.5%) and corrugated & kraft paper (6.1%) are the largest components of
. the recycled waste stream excluding concrete and asphalt.
. Concrete and asphalt are the largest components (by weight) of the waste stream being
disposed of outside the landfill as well as the largest component (by weight) of the
recycled and total waste streams.
. Concrete (43.4%), corrugated & kraft paper (7.0%), food waste (6.8%) and asphalt (6.6%)
are the largest components (by weight) in the "total" waste stream of Saline County.
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. Corrugated & kraft paper, leaves/ other yard waste, and food waste are the largest
components of the potential recyclable waste stream. However, only corrugated & kraft
paper (20.4%) is currently recycled at any significant level in Salina.
Estimated Annual Quantities of the Saline County Waste Stream
Landfilled Recycled Non- Combined Waste
Waste Waste Landfilled Stream (tons/mean)
Stream Stream C&D Waste
(tons) (tons) Stream (tons)
Concrete 957 10 ,ODD 55,000 65,957 43.4%
Corrugated & Kraft 9,312 1,357 0 10,669 7.0%
Food 10,414 0 0 10,414 6.8%
Asohalt 0 7000 3000 10,000 6.6%
CDM Camp Dresser & McKee
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Section 1
Introduction
The City of Salina and Saline County are in the process of updating the County's solid waste
management plan. In order to update the plan, the Solid Waste Management Committee has
identified the need to assess the characteristics of the solid waste generated in the county-wide
study area. This study will include a physical characterization over three seasons of the
residential, commercial, industrial, and construction/ demolition waste generated in the County
and disposed of at the City of Salina Municipal Solid Waste Landfill (MSWLF). The City of
Salina has secured a matching grant from the Kansas Department of Health and Environment
(KDHE) to conduct the study. The goal of this study is to identify those segments of the waste
stream which can be targeted for more effective handling and/ or processing. The following
data are required to accomplish these ends:
. identification by generator of selected waste stream components by weight
percentages;
. identification of the quantities and handling methods of landscape waste,
construction and demolition (C&D) waste, and other materials in the waste stream;
and
. identification of the quantities and handling methods for recovered recyclable
materials and other materials which are not disposed at the City of Salina MSWLF.
This report is a summary of the findings from the three seasonal waste sampling events. The
three seasons represented include fall, winter and a combined spring/ summer season. All of
the events were conducted at the City of Salina MSWLF.
It should be noted that throughout this report many annual figures are presented. These annual
figures take into account that the spring/ summer sampling event is representative of both
spring and summer seasons. Therefore, quantities labled spring/summer represent six (6)
months, while fall and winter represent three (3) months each.
Since the waste characterization study began, certain municipal programs have been enacted
within the City of Salina. Programs such as the diversion of grass clippings to local composting
operations clearly affects the composition and quantity of waste disposed at the City of Salina
MSWLF. During the week of the spring/summer sampling event, the City of Salina diverted an
estimated 82 tons of grass clippings from the landfill. This extrapolates to almost 1,000 tons of
grass clippings over a three month period (corresponding to approximately 13% of the total
residential waste stream tonnage during that period). The diverted grass clippings are not
included in land filled tonnages because the pilot program is not considered to contribute to the
normal waste stream.
CDM Camp Dresser & McKee
1-1
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Section 1
Introduction
Another event that took place in May 1997 was "Free Day" at the City of Salina MSWLF.
During this event, residents of Saline County could dispose of their household wastes at the
landfill at no charge. Approximately 264 tons of mixed waste and 26 tons of yard/landscape
waste was accepted at the landfill during this event. Although "Free Day" is an annual event at
the City of Salina MSWLF, it is not considered a "regular program" which contributes to the
normal waste stream. Therefore, landfilled tonnages do not include material from the "Free
Day" event.
One final anomaly that took place was a hail storm that struck Saline County in late spring.
Violent storms typically generate large quantities of construction/ demolition materials from
damage done to buildings. This is supported by the landfill records, with excessive construction
material tonnages during late May and June (approximately 300 tons in excess of the average
quantity).
For the purpose of this study, these events and community programs are being considered
atypical and will not be included in the results of this report.
The report presents the following information:
. Study Approach (Section 2)
. Landfilled Waste Composition Findings (Section 3)
. Total Waste Stream Composition Findings (Section 4)
. Conclusions and Recommendations (Section 5)
. Solid Waste Characterization Study Workplan (Appendix A)
. Sampling Event Results (Appendix B)
CDM Camp Dresser & McKee
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Section 2
Study Approach
2.1 Introduction
The following tasks were performed as part of the study:
. Audit of current solid waste generation, handling, and disposal practices within Saline
County by conducting phone and personal interviews with area businesses;
. Development of a waste characterization workplan describing the audit and sampling
procedures for the three season sampling events of wastes being disposed at the City
of Salina MSWLF; and
. Performance of three planned sampling events (Fall, Winter, and Spring/Summer).
2.2 Waste Audit
CDM's first task in determining the composition of waste generated in Saline County was to
develop a mass balance of the waste flow in the county. In order to develop the mass
balance it is necessary to understand the hauling and disposal practices, as well as the
quantities of material generated. ['his information is important in determining which
vehicles should be sorted during the sampling events, as well as to identify waste materials
which do not go to the landfill and thus, must be characterized through other methods.
The mass balance is developed through an audit of the generators, haulers, and recyclers of
solid waste. The list of businesses interviewed is shown in Table 2-1. The following
paragraphs will provide an overview of Saline County's solid waste activities developed
through these interviews.
2.2. 1 Landfilled Waste
Prior to conducting the first sampling event, the audit identified hauling practices within the
county. This was necessary to determine the sources of waste materials and thus, determine
which sources should be sampled during the sampling events. The list of haulers
interviewed was compiled from lahdfill records and CDM's knowledge of waste
management practices in the county.
The objective of this stage of the audit is to assure the waste sorted by the CDM crew
accurately represents the characte~istics of the generators in the city and county. This helps
to ensure that waste chosen for sorting does not come from only one part of the county, or
from only one waste stream. It also identifies materials that are disposed through other
methods and therefore, must be identified through other means. To provide this assurance,
the quantities of waste generated ih the county (by material type), the geographical
CDM Camp Dresser & McKee
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Table 2-1
Interviewed Waste Generators, Handlers, and Recyclers
Saline County Waste Audit
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Business Name Typ~ of Materials Handled Contact Name Phone
Busi~ess Number
AAA Builders Generator Constructi onlDemolition Peggy Plumlee 913-823-6521
Ballou Construction Generator ConstructionlDemoli tion Larry Day 913-825-5303
Barnhill Appliance Repair Service Generator White Goods (Other) N.S. Barnhill 913-825-0763
Bill Medina Construction Generator ConstructionlDemolition Steve Reonig 913-825-4561
"
Bos Construction Generator ConstructionlDemolition Terry Holacek 913-823-1334
Busboom & Bauh Construction Generator ConstructionlDemoli tion Bob Miller 913-825-4664
Central Kansas Salvage Recycler Metals (Recycled) Sandy Heath 913-827-5801
Concrete Recycling Recycler Concrete (CID) Steve McGee 913-826-9474
Crane Rental & Erection Service Generator ConstructionlDemolition Rex Russel 913-826-0099
Deihl Construction Generator ConstructionlDemoli tion - 913-823-7800
Dillon's Food Stores Recycler High Value Recyclables Bill Shraug 800-366-2175
Exide Battery Recycler Car Batteries (Recycled) Mark Challans 316-942-3116
Frank Construction Generator ConstructionlDemoli tion Bob O'Neil 913-825-4213
Fuller Scrap Metal Recycler Metals (Recycled) Gary Fuller 913-825-4822
Gimenson Hauling Hauler ResidentiaVCommercial Mr. Gimenson 913-536-4277
Harbin Construction Generator Constructi on/Demoli tion Ross Hoffuines 913-825-1651
Harris Trash & Recycling Hauler ResidentiaVCommercial Mr. Harris 913-823-3996
Images, Inc. Recycler High Value Recyclables Ken Reitz 913-827-0777
Jayhawk Roofing Generator Constructi onlDemolition Randy Worchester 913-825-5446
JH Shear's and Sons Recycler Asphalt (Recycled) Vern Hopkins 913-823-5537
Kmart Discount Stores Generator Car Batteries (Recycled) - 913-825-1591
Mid America Appliance Center Generator White Goods (Other) - 913-825-8925
Nelson Appliances Generator White Goods (Other) - 913-825-7011
Peterson Refuse Hauler ResidentiaVCommercial Philip Peterson 913-225-6704
Quick Cash Recycler High Value Recyclables Craig Miller 913-827-1309
Rapp Construction Generator Construction/Demoli tion Jay Rapp 913-823-1340
Recycle It Hauler All Solid Waste Tom Smith 800-324-8020
Refuse & Recycle Hauler ResidentiaVCommercial Bob Piper 913-823-6137
Salina Appliance Showroom Generator White Goods (Other) Randy 913-827 -1420
Salina Concrete Products Supplier ConstructionlDemolition Jim 913-823-1343
Salina Dept. of General Services Hauler Residential James Hill 913-826-7375
Salina Roofing Generator ConstructionlDemoli tion Dennis Egan 913-827-3204
Salina Waste Hauler All Solid Waste Glen Stroer 913-825-9155
Smoky Hill Generator ConstructionlDemolition Richard Brown 913-825-1224
Tom Egan Roofing Generator Constructi onlDemoli tion Tom Egan 913-825-5886
Walmart Recycler OCC/Car Batteries Sandy Barthalemew 913-825-6800
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SMRYSORTXLS - AUDIT
8/21/97
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Section 2
Waste Generation & Collection Practices
distribution of waste generation, the collection routes of the haulers (both public and
private), and the current levels of recycling were established.
Based on discussions with the identified haulers, CDM determined the individual
companies' hauling routes and set'Vice areas as shown in Table 2-2 and depicted in Figure 2-
1. Since the waste audit was performed in the Fall, Salina Waste System, Inc. has increased
both its hauling capacity and its area of service by purchasing Refuse & Recycle and Recycle
It. Tables 2-1 and 2-2 as well as figure 2-1 have been updated to reflect this change. For the
most part, Salina's residential waste is collected by the City of Salina Department of General
Services (about 75%) and Salina Waste System Inc. (approximately 20%), with the remainder
being collected by several small private haulers (approximately 5%).
Table 2-2
Saline County Hauling Companies
Hauler Phone Number of Collection Service Area
Number Trucks
City of Salina (913) 826-737~ 9 Rear Loaders Residential - Salina
Salina Waste 6 Rear Loaders Residential- Salina & Townships
System, Inc. (913) 825-9155 3 Front Loaders Commercial- Salina & Townships
3 Roll-Offs Industrial- Salina & Townships
Peterson Refuse (913) 225-6704 1 Rear Loader Residential- Salina & Townships
Commercial - Salina
Gimenson (913) 536-4277 2 Rear Loaders Residential- Townships
Hauling Commercial- Townships
Harris Trash & (913) 823-3996 1 Rear Loader Residential - Salina
Recycling, Inc. 1 Roll-Off Commercial - Salina
Both the City's trucks and Salina Waste collect from the same areas of the City on the same
day (as shown in Figure 2-1). Th~ Monday and Tuesday routes include southern Salina.
The Wednesday route focuses on near southwest Salina. The Thursday route covers north
and east Salina and the Friday route includes western Salina.
Commercial and industrial waste collection throughout the County, as well as residential
waste outside the City of Salina, is performed solely by private hauling companies. Salina
Waste collects the majority of the commercial and industrial collections throughout the
county. Much of the waste generated in the townships of Saline County (outside Salina) is
collected by other hauling companies.
CDM Camp Dresser & McKee
2-3
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CITY COLLECTION ROUTES
MONDA Y ROUTES (RESIDENTIAL!
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WEDNESDA Y ROUTES (RESIDENTIAL!
THURSDA Y ROUTES (RESIDENTIAl)
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TOWNSHIP COLLECTION ROUTES
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Figure No. 2-1
RESIDENTIAL & COMMERCIAL COLLECTION ROUTES
SALINE COUNTY HAULERS
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Section 2
Waste Generation & Collection Practices
Waste collected in the county is o/pically disposed at the City of Salina MSWLF. Trucks
with mechanized tipping capabilities bring waste directly to the active disp'osal area at the
landfill. Other vehicles dispose the refuse at one of four 30 cubic yard containers in the
landfill convenience area located adjacent the scale house. This area typically receives large
quantities of landscaping and construction! demolition material.
2.2.2 Construction and Demolition (C&D) Waste
A significant portion of the waste. generated in the County is not disposed of at the City of
Salina MSWLF. This includes materials generated in Salina which is recycled. Material
generated from construction/ demolition activities is being handled by other methods of
disposal.
The C&D waste is typically comprised of concrete, wood (treated and untreated), asphalt,
roofing materials, drywall, corrugated cardboard, soil, and metals. Interviews with general
contractors and material suppliers indicated that the high tipping fees at the landfill,
especially for concrete, has forced contractors to find other methods of disposal for some of
these wastes. Land application of waste at nearby farms was found to be a common method
of disposal for many contractors.
Other handling methods for C&D waste include re-use, recycling, and disposing at other
area landfills (see Table 2-3). Some efforts have been made to recycle concrete and asphalt.
Concrete Recycling, the only known concrete crushing plant in Saline County, crushes
concrete for the production of stone materials. I.H. Shear's and Sons is an asphalt supplier
that recycles milled asphalt waste from their road construction projects for use in their hot
mix asphalt plant.
CDM determined the total quantity of C&D materials being generated within Saline County
through phone interviews. However, the interviews found the contractors do not maintain a
detailed breakdown of waste materials.
Roofing contractors generally were able to provide requested information. Typically,
roofing contractors within Saline County dispose of their waste at the City of Salina MSWLF.
The material is most commonly comprised of tar paper, asphalt shingles and occasional
large quantities of wood.
2.2.3 Recycled Materials
Another source of waste being generated, and not landfilled, is recycled materials (other
than from C&D activities). Interviews were conducted :with local scrap metal recyclers,
recycling centers, and businesses that participated in or processed materials from recycling
programs. The information collected from the interviewees indicated besides the ongoing
concrete and asphalt recycling, the most commonly recycled materials are ferrous metals,
corrugated cardboard and kraft paper, car batteries, aluminum, and newsprint (see Table 2-
4). Local businesses participating in in-house recycling efforts (excluding recycling centers)
include Wal-Mart (corrugated cardboard and car batteries), Tony's Pizza (corrugated
cardboard), and Exide Battery Warehouse (car batteries).
CDM Camp Dresser & McKee
2-5
Table 2-3
Current Handling Methods for C/D Materials in Saline County
Concrete Aspha Woo ar oar 00 Ing e as 01 rywa
Back Fill . D D D D D . D
Burn * * . D D * * *
Re-Use * D D D * D . D
Recycle D . D . D . D D
Salina Landfill D D D D . D D .
Out-of-County D D D D D D D D
Landfill
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. Very Common
Q Common
D Not Common
* Not Applicable
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Section 2
Waste Generation & Collection Practices
Table 2-4
Current Annual Tonnages of Recycled Materials in Saline County*
(not including recycled C&D materials)
Fall 1996
Ferrous Metal 1450 Clear HDPE Containers 28
Cardboard & Kraft Paper 1351 PET Bottles 21
Car Batteries 779 Brown Glass Containers 15
Aluminum Scrap 510 Magazines 15
Newsprint 410 Green Glass Containers 12
Aluminum Cans 402 High-Grade Paper 12
Non-Ferrous Metal 95 Polyethylene Film 9
Clear Glass Containers 36 Colored HDPE 7
Low-Grade Paper 30 Polystyrene Foam 2
Tin-Steel Bimetal Cans 30
"Quantities shown obtained from solid waste audit.
Note: White Goods and Tires collected at City of Salina MSWLF not included
2.3 Sampling Event Workplan
Prior to the Fall sampling event, a waste characterization study project workplan was
developed by CDM. The workplan addressed study approach, waste generation and
collection practices, waste characterization procedures, data recording, and health and safety
issues. A copy of this plan is provided in Appendix A.
As described in the workplan, the residential and commercial portions of the waste stream
were characterized through the manual sorting of random samples from pre-selected
collection vehicles that the available data indicated were representative of the residential
and commercial waste generated in Saline County. The samples were sorted into 38
material categories, which are presented as follows:
· Newsprint.
· Corrugated cardboard and kraft paper.
· High-grade paper.
· Magazines.
· Other paper.
· PET (polyethylene terephthalate) bottles.
· Clear HOPE (high-density polyethylene) containers.
. Colored HOPE (high-density polyethylene) containers.
CDM Camp Dresser & McKee
2-7
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Section 2
Waste Generation & Collection Practices
. Other plastic containers.
. Polyethylene film.
. Polystyrene foam.
. Other plastic.
. Food waste.
. Grass clippings
. Leaves/Other yard waste
. Wood
. Treated lumber
. Textiles, rubber, and leather
. Disposable diapers
. Fines
. Aluminum cans
. Aluminum scrap
. Other nonferrous metal
. Tin-steel and bimetal cans
. Ferrous metal
. Batteries
. Clear glass containers
. Brown glass containers
. Green glass containers
. Other non-recyclable glass
. Other combustibles/noncombustibles
. Roofing materials
. Metal
. Concrete
. Bricks
. Blocks
. Gypsum board and plaster
. White Goods
After the samples had been sorted into the specific material categories, the weight of each
material for each sample was obtained and recorded.
The city residential samples were obtained each day during the sampling event so that
residential waste from pre-determined geographic areas within the city were represented.
Since few trucks are needed to collect refuse generated in the townships, generally all
township collection routes were sampled and sorted. The annual quantities of the various
waste streams from the 1995 City of Salina MSWLF records were used to apportion the
number of samples to be collected in this study. Data showed approximately a 3:2 ratio of
residential to commercial waste for Saline County. This ratio was confirmed after each
sampling event.
Sampling events were conducted from November 11, 1996, to November 15, 1996 (Fall
Event), February 17, 1997, to February 21, 1997 (Winter Event), and May 12, 1997 to May 16,
1997 (Spring/Summer Event). Waste samples were obtained from selected hauling vehicles
entering the Salina MSWLF. A total of 133 samples were collected during the three
CDM Camp Dresser & McKee
2-8
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Section 2
Waste Generation & Collection Practices
sampling events: 77 from residential sources and 56 from commercial sources.
Approximately 24,700 pounds of residential and commercial waste were sorted during these
sampling events. Weights of the samples ranged from 80 to 580 pounds with an average
sample weight of approximately 186 pounds.
Industrial loads and landfill convenience area wastes were characterized through visual
analysis of vehicle loads and from gate forms completed by landfill personnel. The
information collected included a description of all loads entering the City of Salina MSWLF
during the week of the sampling events. The composition for the Landfilled waste stream is
provided in Section 3 of this report, while the Total waste stream is provided in Section 4 of
this report.
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CDM Camp Dresser & McKee
2-9
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Section 3
Landfilled Waste Composition Findings
3.1 Introduction
The Saline County waste stream is comprised of materials generated by residential,
commercial, industrial, and construction/ demolition sources. The largest percentage of
material by weight is generated by the construction/ demolition industry, although most of
these wastes do not enter the City of Salina MSWLF. This is followed by residential,
industrial, and commercial materials. The largest percentages of materials by weight that
enter the landfill are food waste, corrugated cardboard, and other paper, attributed to the
residential, industrial, and commercial sectors. The following is a detailed description of the
landfilled waste streams.
3.2 "Landfilled" Material Waste Streams
3.2. 1 Residential Waste Stream
The residential waste stream is defined as solid waste collected by City and private haulers
from residential units and disposed at the MSWLF. A small amount of residential waste is
self-hauled to the City of Salina MSWLF. This does not represent 100% of the waste
generated by the residential community. Some materials are segregated and handled prior
to disposal at the landfill (e.g., recycling centers). The sampling event at the City of Salina
MSWLF provided data on the composition of this waste stream. Samples were taken from
vehicles hauling residential routes both in the City of Salina and the townships of Saline
County.
Data from the sampling events indicated the majority of the waste was comprised of leaves
and other yard waste, other paper, food waste, kraft paper and corrugated cardboard, and
newsprint. The most abundant material (by weight) was leaves and other yard waste, which
are commonly disposed of during the fall and spring months. The grass clippings which
began to be diverted to composting operations in the spring are not included in landfilled
tonnage figures because the pilot program is not representative of the normal waste stream.
Percentage by weight of leaves and other yard waste is most likely relatively high due to
spring cleaning. The actual average percentage by weight over spring and summer is
probably lower. A detailed material distribution of the residential waste stream is shown in
Figure 3-1..
3.2.2 Commercial Waste Stream
For this report, commercial waste is defined as solid waste generated by commercial
businesses within Saline County and brought to the MSWLF. Some of this waste is also
segregated and handled prior to disposal at the landfill (e.g., recyclable materials).
CDM Camp Dresser & McKee
3-1
Leaves / Oiller Yard Waste
Other Paper
Food Waste
Corrugated & Kraft Paper
Newsprint
Textiles, Rubber, & Leather
Polyeillylene Film
Disposable Diapers
Grass Clippings
Nlagazincs
Tin-Steel & Bimetal Cans
Other Plastic
Clear Glass COlllainers
Clean Wood
Ferrous Metal
Colored HDPE Containers
Aluminum Cans
Clear HOPE Containers
Other Plastic Containers
Polystyrene Foam
High-Grade Paper
Brown Glass Containers
PET Boules
Concrete
Treated Lumber
Oiller Non-Ferrous Metal
Roofing Materials
Green Glass Containers
Aluminum Scrap
Gypsum Board & Plaster
OilIer Glass
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Section 3
Composition Sampling Events
Recycling is typical of larger businesses handling large quantities of a recyclable material
(e.g., corrugated cardboard recycled at Wal-Mart) or by those needing to dispose of a
material banned from landfills (e.g., car batteries). Samples were obtained from vehicles
serving commercial routes both in the City of Salina and the townships of Saline County.
Data from the sampling events indicated the majority of the commercial waste was
comprised of kraft paper and corrugated cardboard, food waste, low grade (other) paper,
and polyethylene film (see Appendix B). Corrugated cardboard and food waste were the
most abundant, typically originating from food service businesses. A detailed material
distribution of this waste is provided in Figure 3-2.
3.2.3/ndustria/ Waste Stream
Waste included in this waste stream is generated by industry within Saline County and
brought to the MSWLF. Most of the waste originates from Tony's Pizza and Philip's
Lighting. Tony's Pizza waste contains mostly food waste, corrugated cardboard, and
polyethylene film, with some paper and aluminum scrap. The majority of Philip's Lighting
waste is glass typical of florescent light bulbs.
A detailed material distribution of this waste stream is provided in Figure 3-3. This data
was obtained from visual characterizations of the waste, information gathered by scale
house personnel, and tipping records for the weeks of the sampling events. The category
"Other Industrial" in the fall event as identified in Figure 3-3 considers all industrial waste
not originating from either Tony's Pizza or Philip's Lighting. This material comprises less
than 20% of the industrial waste stream and 3% of the overall waste generated in Saline
County. Based on the winter and spring/summer sorts, the "other industrial" category was
assumed to consist of 50% corrugated cardboard and kraft paper, 40% clean wood, and 10%
other paper.
3.2.4 Construction/Demolition Waste Stream
For this study, the C&D waste stream is defined as waste generated from
construction/ demolition activities within Saline County and brought to the MSWLF. The
waste audit determined that only a small portion of the total quantity generated is being
disposed at the City of Salina MSWLF. Conversations with general contractors, roofing
contractors, material suppliers, and concrete and asphalt recyclers provided insight into the
disposal practices of construction/ demolition contractors (see Table 2-3).
Due to the bulky nature of the waste, this material was not manually separated during the
sampling event. Data was obtained from visual characterizations of the waste, information
gathered by scale house personnel, and tipping records for the weeks of the sampling
events. A detailed material distribution of this waste stream is shown in Figure 3-4.
CDM Camp Dresser & McKee
3-3
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Otllcr Plastic
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Ncwsprinl
I Lcavcs I Otllcr Yard Wastc
Fcrrous Mctal
I
High-Gradc Papcr
Tin-Stcel & Bimctal Cans
I
Gypsum Board & Plastcr
Roofing Matcrials
I
Grass Clippings
Otllcr Non-Fcrrous Metal
I
Brown Glass Containers
Polystyrene Fomn
Disposable Diapers
I
Aluminum Scrap
Clear Glass Containers
I
Aluminum Cans
Colored HOPE Containers
I
Other Plastic Containers
Concretc
I
Magazines
PET Bottles
Clear HOPE Containers
I
Other Glass
Treated Lumber
I
Batteries
Green Glass Containers
()
I~
I
Percentage (Weight)
o
o
~
VI
o
~
""
.....
9
o
~
Fincs
Otllcr
Mctal
.....
VI
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<= -<
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r
Figure 3-3
Composition Of Industrial Waste Stream By Weight
35.00/0 -----.----..------...---.. .-~_..._------~._~---~-_._-_..
30.0%
5.0%
_ Fall Sampling Event
_ Winter Sampling Event
_ Spring/Summer* Sampling Event
___ Annual* Mean
25.0%
* Spring/Summer values represent spring and summer
seasons combined (6 months).
r-.
.....
.c
.':P 20.0%
~
~
'-'
~
OJ)
~
.....
t::
~ 15.0%
loo
~
Q.,
10.0%
0.0% ... 0- '-' or. ... ~
or. ... -0 ... E .~ -;a '-' "2 ~ <:.>
; '" <:.> 0 '-' !i ~ e .~ 0-
9- 0 9- i.i: <:.> g 0 .. ~
~ "-
~ 0 6:: ~ 6:: 0: 0 C/.l or.
% or. ,...l S :: 0 '-' -g
... ~ ... <.) U .~ -0
-0 '" ~ ;:; ... ::> o(j .~ Z
0 -5 ~ '" ;;.. ~ g ~ ... ;>:
0 ..: 't
tL 0 U v -5 v <:.> <:.> ...
o(j '" tL .0 :; en '"
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-0 0 ::> :i 0
~ "- i=<:
'" '"
00 '"
E '"
'3 :::
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E-
_ 1;:f..IfD_TYT _To;,;trl~\l Gnlnb... 8/21/97
- - - - - - - - - - - - - - -
70.0%
60.0%
50.0%
,-...
....
-=
.~ 40.0%
~
~
~
Oil
~
....
c
~ 30.0%
I.
~
Q.
20.0%
10.0%
-
Figure 3-4
Composition Of Construction! Demolition Waste Stream By Weight
_ Fall Sampling Event
_ Winter Sampling Event
_ Spring/Summer* Sampling Event
___ Annual* Mean
* Spring/Summer values represent spring and summer
seasons combined (6 montbs).
0.0% e '"
~ ~ 3 ~ ~ !> ~
~ ~ '" ~ ~ lL
~ g. " :20
g 0:: ~ :20 C/J ;,l '"
g 0: 0 ...l '" "5 a ~ ::; t5 ::l
~ o<J u o<J ::l .5 1:j >- ~ g
~ ~ ~ E ;;:: C -5 v '"
~n U 5 '" ~ a '" ~
0 o<J .<; l1.. '" ::l ~
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Section 3
Composition Sampling Events
3.2.5 Combined "Landfilled" Wastes
The material percentage compositions from the four landfilled waste streams were
combined in orderto estimate the composition of waste currently being landfilled in the City
of Salina MSWLF. The quantities of the various waste streams are based on Salina landfill
tipping records for Fall 1996, Winter 1997, and Spring/Summer 1997 and information
obtained during the waste audit from the generators, haulers, and recyclers. These reports
provided tonnages on the landfilled waste streams as shown in Table 3-1. Percent
compositions using sampling event data were multiplied by these quantities to provide an
approximate seasonal tonnage for each of the materials.
Table 3-1
Annual Landfilled Quantities By Material Type
City of Salimi MSWLF 1996-1997 Records (in Tons)
Fall Winter Spring! Annual Annual %
Summer* Total
Residential 6,296 4,592 6,920 24,728 32.1%
Commercial 4,202 3,545 4,331 16,409 22.1%
Industrial 6,459 4,502 5,001 20,963 29.1%
Construction 2,309 1,579 2,722 9,332 11.8%
Other 845 54 2,163 5,225 4.9%
Total 20,111 14,271 21,136 76,654 100.0%
* Spring/Summer values are assumed to represent spring and summer seasons combine. This represents six (6) months, while
other seasons represent three (3) months.
The combined data (see Table 3-2) show the largest percentage of materials by weight are:
- Food Waste (14.7%),
- Corrugated Cardboard & Kraft Paper (13.4%),
- Other Paper (8.6%).
- Other Glass (7.6%),
- Leaves & Other Yard Waste (7.5%), and
- Clean Wood (7.2%).
Figure 3-5 provides a more detailed breakdown of the combined waste stream by material
type.
CDM Camp Dresser & McKee
3-7
I
I
I
I
Food Waste
I Corrugated & Kraft Paper
Other Paper
Other Glass
I Leaves I Other Yard Waste
Clean Wood
Roofing Materials
'I Polyethylene Film
Textiles, Rubber, & Leather
Fines
I' Newsprint
Other Plastic
Gypsum Board & Plaster
I Ferrous Metal
Other
Concrete
I Disposable Diapers
Grass Clippings
Magazines
I: Tin-Steel & Bimetal Cans
Clear Glass Containers
High-Grade Paper
I Aluminum Scrap
Polystyrene Foam
Brown Glass Containers
Aluminum Cans
I Other Non-Ferrous Metal
Colored HDPE Containers
Other Plastic Containers
I Clear HDPE Containers
PET Bottles
Treated Lumber
I Green Glass Containers
Batteries
Metal
I Bricks
Asphalt
Blocks
I Car Batteries
Tires
White Goods
TOTAL
I
Table 3-2
Statistical Analysis of LandfilIed Waste Stream
Fall
..
u
.. c
.5 ..
't:l
'E. 't:l C c
E c
.. 0 0-
.. ('I; U :
"'~ 't:l ..
C C .- lI<~
= .. ~&
~~ <:> c
01_
16.5% 2.3% 0.9%
13.1% 11.0% 4.4%
7.3% 0.3% 0.1%
10.9% 3.6% 1.4%
7.9% 9.6% 3.8%
5.3% 1.0% 0.4%
7.6% 0.7% 0.3%
4.7% 0.7% 0.3%
2.4% 0.1% 0.0%
4.1% 0.1% 0.0%
2.8% 3.2% 1.3%
1.4% 0.6% 0.2%
2.4% 0.0% 0.0%
0.9% 4.6% 1.9%
1.3% 0.7% 0.3%
0.8% 0.0% 0.0%
J.l% 5.1% 2.0%
0.3% 6.1% 2.4%
J.l% 0.0% 0.0%
1.2% 0.5% 0.2%
0.7% 1.2% 0.5%
0.8% 1.2% 0.5%
1.4% 5.4% 2.2%
0.4% 2.9% 1.2%
0.2% 12.4% 4.9%
0.3% 1.8% 0.7%
0.3% 0.4% 0.2%
0.3% 1.4% 0.6%
0.6% 0.5% 0.2%
0.3% 0.0% 0.0%
0.2% 8.6% 3.4%
0.2% 0.0% 0.0%
0.1% 8.2% 3.3%
0.1% 0.9% 0.4%
0.2% 10.6% 4.2%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
. 0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
100.0% 0.0% 0.0%
SMRYSORT.XLS . Landfilled
. SpringlSununer Tonnages are assumed to represent both Spring and Summer
TOIUlages,l.hcrefnre the value is counted twice for Armual Tonnages.
I
Winter
c: ..
u
.. C
.. ..
Iol 't:l
.. 't:l C '2
&. .5 .. 0 o-
ct':.:; u :
~c. 't:l .. lI<~
.5 E ~ 'E
~ ,~ <:> c
",Q 01_
16.2% 1.7% 0.7%
18.1% 9.3% 3.6%
9.8% 11.4% 4.4%
6.7% 13.0% 5.0%
1.8% 0.0% 0.0%
8.5% 0.4% 0.2%
1.7% 0.0% 0.0%
5.0% 2.4% 0.9%
4.2% 3.3% 1.3%
3.2% 1.3% 0.5%
3.3% 0.0% 0.0%
3.6% 4.1% 1.6%
2.2% 0.0% 0.0%
2.9% 0.0% 0.0%
1.8% 5.8% 2.3%
1.5% 0.0% 0.0%
1.6% 0.8% 0.3%
0.0% 2.7% 1.0%
0.9% 0.0% 0.0%
1.2% 0.4% 0.1%
1.0% 8.8% 3.4%
1.3% 4.1% 1.6%
0.2% 0.6% 0.2%
0.5% 2.0% 0.8%
0.5% 0.7% 0.3%
0.4% 0.5% 0.2%
0.3% 7.9% 3.1%
0.3% 5.1% 2.0%
0.3% 4.8% 1.9%
0.3% 0.0% 0.0%
0.3% 1.1% 0.4%
0.0% 0.0% 0.0%
0.1% 2.1% 0.8%
0.1% 0.0% 0.0%
0.0% 10.1% 3.9%
0.0% 0.0% 0.0%
0.0% 1.8% 0.7%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
100.0% 0.0% 0.0%
SDrimuSummer
.. ..
.. u
E c
..
E .. 't:l
C
= C 't:l C C
"'= .. 0 0-
ObE'~ ('I; U :
't:l ..
oE C'lI 5 c;;: ~ t
r~~ [~ ~~ 2]
13.1% J.l% 0.4%
11.3% 2.7% 1.0%
8.7% 15.2% 5.5%
6.4% 7.5% 2.7%
10.1% 0.0% 0.0%
7.4% 0.4% 0.1%
5.4% 10.7% 3.9%
4.3% 6.5% 2.3%
3.7% 4.9% 1.8%
3.2% J.l% 0.4%
2.9% 0.5% 0.2%
3.2% 5.4% 1.9%
2.5% 0.2% 0.1%
2.4% 6.2% 2.2%
1.5% 2.6% 0.9%
1.8% 0.2% 0.1%
1.5% 4.9% 1.8%
2.4% 6.8% 2.4%
1.4% 5.5% 2.0%
1.0% 0.4% 0.1%
0.8% 3.8% 1.4%
0.4% 2.2% 0.8%
0.5% 2.3% 0.8%
0.4% 6.0% 2.1%
0.5% 1.0% 0.4%
0.5% 1.5% 0.5%
0.5% 12.3% 4.4%
0.6% 5.2% 1.9%
0.3% 6.9% 2.5%
0.4% 0.0% 0.0%
0.3% 0.8% 0.3%
0.4% 0.2% 0.1%
0.1% 2.1% 0.8%
0.1% 2.4% 0.8%
0.0% 4.6% 1.7%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
100.0% 0.0% 0.0%
Combined Event A vera2e
..
c u
c
il ..
't:l
::;; C
* "E g c
0-
-; ct 0'::: U :
= 't:l .. ~~
C c'.
c ,~ & <:> C
-< 01 _
14.7% 1.9% 1.5%
13.4% 3.2% 2.6%
8.6% 1.0% 0.9%
7.6% 2.2% 1.8%
7.5% 3.9% 3.2%
7.2% 1.3% 1.1%
5.0% 2.5% 2.0%
4.6% 0.4% 0.3%
3.5% 0.8% 0.6%
3.4% 0.5% 0.4%
3.0% 0.2% 0.2%
2.9% 1.0% 0.8%
2.4% 0.2% 0.1%
2.2% 0.8% 0.7%
1.5% 0.2% 0.1%
1.5% 0.5% 0.4%
1.4% 0.2% 0.2%
1.3% 1.3% 1.0%
1.2% 0.2% 0.2%
1.1% 0.1% 0.1%
0.8% 0.1% 0.1%
0.7% 0.4% 0.4%
0.7% 0.5% 0.4%
0.5% 0.0% 0.0%
0.4% 0.1% 0.1%
0.4% 0.1% 0.1%
0.4% 0.1% 0.1%
0.4% 0.1% 0.1%
0.4% 0.2% 0.1%
0.4% 0.0% 0.0%
0.3% 0.0% 0.0%
0.3% 0.2% 0.2%
0.1% 0.0% 0.0%
0.1% 0.0% 0.0%
0.1% 0.1% 0.1%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
0.0% 0.0% 0.0%
100.0% 0.0% 0.0%
8/21197
I
"
'"
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c 0 N :l'"
I~ 0 0 0
;::;Q ;::;Q ;::;Q
-1
~ Food Wastc
Ii Corrugalcd & Kraft Papcr
...
F Othcr Papcr
If Olhcr Glass
Lcavcs / OUlcr Yard Wastc
I Clclm Wood
Rooling Matcrials
I PolycUlylcnc Film
Textilcs, Rubbcr, & LcaUlcr
Fincs
I Ncwsprim
Othcr Plaslic
I Gypsum Board & Plaslcr
Fcrrous Mctal
I Olhcr
Concrctc
I Disposablc Diapcrs
Grass Clippings
Magazines
I Tin-Slcel & Bimclal Cans
Clcar Glass Conlainers
I High-Gradc Papcr
Aluminum Scrap
I Polystyrcnc Foam
Brown Glass Containcrs
Aluminum Cans
I OUlcr Non-Fcrrous Mctal
Colorcd HDPE Containcrs
I Othcr PlasLic ConLaincrs
Clcar HDPE ConUliners
I PET BoLtlcs
TrcaLcd Lumbcr
I Grcen Glass Containcrs
Ballcrics
00 Metal
I~
\C Bricks
-J
I
Percentage (Weight)
...... ...... ...... N
0\ ;x> 0 N .j:;>. 0\ 00 0
0 0 0 0 0 0 0 0
;::;Q ;::;Q ;::;Q ;::;Q ;::;Q ~ ;::;Q ;::;Q
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:= (D C/J
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C/J C/J
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C/J tTl (tl
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Section 4
Total Waste Stream Compositions Findings
4.1 "Non-Landfilled" Material Waste Streams
4. 1. 1 Recycled Waste Stream
A portion of the waste generated in Saline County is currently recycled. The recycled waste
stream is defined as materials generated within Saline County and brought to scrap metal
recyclers, centralized recycling centers, and C&D material recycling plants (e.g., concrete
crushing plant). The material is comprised largely of concrete and asphalt which are recycled at
crushing plants and material suppliers of these materials. In addition, ferrous metal, corrugated
cardboard and kraft paper, and car batteries are commonly recycled.
By definition, this material is not being disposed of at landfills, therefore CDM determined the
approximate annual quantities of the waste through interviews with generators and processors.
The material distribution of this waste stream, as shown in Figure 4-1, is based on these
interviews.
4. 1.2 "Other" C&D Waste Stream
This waste stream is comprised of materials generated from C&D activities within Saline
County and ~isposed of by some other means than land filling or recycling. Examples of
materials in this waste stream include concrete and asphalt disposed at sand pits or open land.
Annual tonnages for these materials were estimated during the waste audit and are provided in
Table 4-1.
Table 4-1
Fall Quarter Tonnages of "Other" C&D Materials*
Waste Material Quantity (tons)
Concrete 13,750
Asphalt 750
Clean Wood 107
*Quantities shown obtained from solid waste audit
CDM <:amp Dresser & McKee
4-1
Asphalt
Ferrous Metal
Corrugated & Kraft Paper
Car Batteries
Aluminum Scrap -.
Newsprint -.
Altiminum Cans
Other Non-Ferrous Metal
Clear Glass Containers
Other Paper
Tin-Steel & Bimetal Cans
Clear HDPE Containers
PET Bottles
Brown Glass Containers
Magazines
Green Glass Containers
High-Grade Paper
Polyethylene Film
Colored HDPE Containers
00
N
-
\0
-.J
Polystyrene Foam
o
V\
o
V\
w
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4.2 Combined Total Generated Wastes
Material quantities from all six of the waste streams, landfilled and non-Iandfilled, were
combined in order to determine the overall composition of waste currently being generated
within Saline County. Percent compositions using sampling event data were multiplied by
Salina MSWLF disposal quantities to provide an approximate seasonal tonnage for each of the
materials. The combined data of all county waste streams (see Table 4-2) show the largest
percentage of materials by weight are:
- Concrete (43.4%)/
- Corrugated Cardboard & Kraft Paper (7.0%)/
- Food Waste (6.8%)/
- Asphalt (6.6%)/
- Other Paper (3.9%)/ and
- Clean Wood (3.8%).
- Leaves & Other Yard Waste (3.8%).
Figure 4-2 provides a more detailed breakdown of the combined total generated wastes by
material type. Note that the Spring/Summer event was assumed to represent both spring and
summer seasons, therefore the Spring/Summer values were counted twice when calculating the
annual means and totals.
CDM Camp Dresser & McKee
4-3
I
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SMRYSORTXLS - COMBINED
Concrete
Corrugated & Kraft Paper
Food Waste
Asphalt
Other Paper
Clean Wood
Leaves I Other Yard Waste
Other Glass
Roofing Materials
Polyethylene Film
Fines
Ferrous Metal
Newsprint
Textiles, Rubber, & Leather
Other Plastic
Gypsum Board & Plaster
Other
Aluminum Scrap
Tin-Steel & Bimetal Cans
Disposable Diapers
Car Batteries
Magazines
Aluminum Cans
Clear Glass Containers
High-Grade Paper
Grass Clippings
Polystyrene Foam
Other Plastic Containers
Other Non-Ferrous Metal
Brown Glass Containers
Colored HDPE Containers
Clear HDPE Containers
White Goods
PET Bottles
Metal
Batteries
Green Glass Containers
Treated Lumber
Tires
Bricks
Blocks
TOTAL
0;
""
"0
~ .,
" OJ)
E ~
~ g
WE-
663
160
1,325
1
76
219
524
31
425
233
154
12
193
14
149
180
6,296
..
.,
"
~
"0
., .,
OJ OJ)
E ~
~ g
WE-
599
620
171
39
97
47
61
52
61
12
27
42
39
22
31
7
10
2
4,592
Residential
*
..
.,
E
E
"0 ::l
~~~
E c ~
".:::; "C c
W ~~
437
452
483
117
967
1
55
159
382
23
310
170
112
9
141
10
108
131
125 376
28
70
34
44
38
45
9
19
31
28
16
22
5
7
1,316
1,363
0;
::l
C
C
<:
"0
., .,
OJ OJ)
E ~
~ g
WE-
o
2,351
2,436
o
2,603
629
5,205
3
298
858
2,059
124
1,671
915
603
49
758
55
583
706
o
671
151
379
185
238
203
241
49
104
167
153
o
87
121
27
39
o
o
6
o
1,457
352
2,913
2
167
480
1,153
69
935
512
337
27
424
31
326
395
85
212
104
133
113
135
27
58
93
85
49
68
15
22
4
13,839 24,727
... Spring/Summer compositions are assumed to represent both Spring and Summer
therefore the Spring/Summer values are counted twice when calculating Tonnages.
0;
""
"0
., .,
~ ~
,g g
~~
4,202
Commercial
..
.,
"
~
"0
., '"
OJ OJ)
E ~
.~ g
WE-
783
699
440
156
89
1
8
334
274
143
110
188
100
159
61
132
81
37
38
22
32
85
3
33
49
34
12
23
21
16
15
10
2
12
3,545
Table 4-2
Composition of Combined Total Generated Wastes By Weight
786
391
*
..
.,
E
E
"0 ::l
~~~
.g .~ a
w ~~
]]6
1,363
1,303
430
254
24
o
230
182
127
128
184
243
81
62
7
51
10
19
29
25
115
40
24
29
32
13
10
9
12
o
1,199
298
307
64
220
506
359
72
203
324
281
21
393
12
166
116
0;
::l
C
C
<:
"0
~ .,
" ~
,g g
~~
116
2,932
2,393
o
2,069
708
420
65
228
1,070
815
342
440
696
624
261
516
151
298
163
o
78
124
147
313
211
172
120
196
186
126
70
o
72
18
51
19
59
o
4
4
21
73
90
113
208
99
47
133
143
91
39
47
4
29
17
47
4
4
8,531
16,l2L
0;
""
"0
~ .,
" ~
-~ g
~~
1,096
1.879
..
.,
"
~
"0
~ '"
" ~
~ g
~~
78
948
1,110
420
475
2,120
368
100
6,459
Industrial
*
..
'"
E
E
"0 ::l
~~~
E c ~
".::"C t::
'" Q, 0
WooE-
312
418
942
234
556
1
588
109
91 202
172 675
165
10 53
19
4,501
1,600
2,595
0;
::l
C
C
<:
"Q
'" '"
OJ OJ)
E ~
~ g
WE-
78
3,645
5,585
o
1,230
1,579
19
5,477
o
1,157
1
753
109
293
848
o
o
164
o
o
o
o
o
o
28
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
497
685
19
2,415
9
10,006 20,966
Construction! Demolition
0;
""
"Q
., .,
OJ OJ)
E ~
t; g
WE-
157
47
..
.,
"
~
"Q
~ .,
" OJ)
E ~
~ g
WE-
137
191
422
8
4 1
1,393
32
10
213
12
4
2,309
*
..
'"
E
E
"Q ::l
.:: CIJ ~
Ebh~
~"t 2
w ~~
21
491
59
239
30
69
1 1
69
39
227
2
2
1,579
469
146
0;
::l
C
C
<:
"Q
~ .,
" ~
-~ g
~~
763
384
o
o
22
2,592
67
5
3,511
36
8
148
2
262
49
1,362
o
102
o
o
o
o
o
o
2
o
o
o
12
o
o
o
o
o
o
o
o
4
o
o
o
1
1.679
1
1,879
5
79
161
922
100
5,443
9,330
Recycled
0;
::l
C
C
<:
"Q
'" .,
~ ~
~ a
~~
10 ,000
1.357
o
7,000
30
o
o
o
o
9
o
1,450
410
o
o
o
o
510
30
o
779
15
402
36
12
o
2
o
95
15
7
28
232
21
o
o
12
o
19
o
o
22,452
Non.Lanfilled CID
0;
::l
C
C
<:
"0
., "
OJ OJ)
E ~
~ g
W...
55,000
o
o
3,000
o
320
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
o
58,320
Combined
0; ., ~
OJ) C
'0 " c
c
... c <: '"
"Q 0 '"
"Q OJ)
'" ... ., "
- - OJ "
" "
E ::l ,~ .,
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-.; c ~ .,
W<: Q,.
65,957 43.4 %
10,669 7.0%
10,414 6.8%
10,000 6.6%
5,954 3.9%
5,827 3,8%
5,711 3.8%
5,550 3,6%
4,038 2.7%
3,131 2.1%
2,884 1.9%
2,817 1.9%
2,632 1.7%
2,167 1.4%
2,123 1.4%
1,671 1.1%
1,274 0.8%
982 0.6%
911 0.6%
870 0.6%
779 0.5%
765 0.5%
677 0.4%
563 0.4%
540 0.4%
449 0.3%
376 0.2%
361 0.2%
352 0.2%
305 0,2%
300 0.2%
250 0.2%
232 0.2%
179 0.1%
139 0.1%
79 0.1%
70 0.0%
63 0.0%
19 0.0%
10 0.0%
4 0.0%
152,073 100.0%
8/21/97
CIl
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......
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Corrugated & Kraft Paper
Concrete ''''''....r..
Food Waste ~~ .-"',
Asphalt . c~" "","1
OUler Paper -."
Clean Wood ""W~~
Other G lass ~
Leaves I OUler Yard Waste =~'"'
Roofing Materials
PolyeUlylene Film
Ferrous Metal
Newsprint
Textiles, Rubber, & LeaUlCr
Other Plastic
Gypsum Board & Plaster ~
Aluminum Scrap
Tin-Steel & Bimetal Cans
Disposable Diapers
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Grass Clippings
Polystyrene Fmml
Other Plastic Containers
OUler Non-Ferrous Metal
Brown Gl:L~S Containers
Colored HOPE Containers
Clear HDPE Containers
White Goods
PET Bottles
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Other
Metal
......
o U\
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Section 5
Conclusions and Recommendations
5.1 Conclusions
. A significant portion (by weight) of the waste generated in Saline County is not disposed
of at the City of Salina MSWLF. Some is being recycled, but most material generated
from construction/ demolition activities is being handled by other methods of disposal
which were not quantified as part of this study.
. Residential waste makes up 32% of the waste going into the City of Salina MSWLF.
. Commercial waste makes up 21 % of the waste going into the City of Salina MSWLF.
. Industrial waste makes up 27% of the waste going into the City of Salina MSWLF.
. Construction waste makes up 12% of the waste going into the City of Salina MSWLF.
. The majority of residential waste is comprised of leaves and other yard waste, (other)
paper, food waste, corrugated & kraft paper and newsprint.
. The majority of commercial waste is comprised of corrugated & kraft paper, food waste,
(other) paper, and polyethylene film.
. The majority of industrial waste is comprised of food waste, other glass, corrugated &
kraft paper, clean wood and (other) paper~
. The majority of C&D waste is comprised of roofing materials, clean wood, gypsum
board/plaster, and concrete.
. Of the total waste entering the City of Salina MSWLF, the majority is comprised of food
waste, corrugated cardboard and kraft paper, (other) paper, other glass, leaves & other
yard waste, and clean wood.
. The total waste stream of Saline County, which also includes items NOT being disposed
of at the landfill, is disproportionately influenced by weighty items such as concrete and
asphalt.
. Although a large quantity of material from the residential and commercial waste streams
is already recycled, that number could increase if the recyclable items of the residential
and commercial waste streams are diverted. Table 5-1 and Figure 5-1 list potential
recyclable items currently being landfilled and/ or recycled. Ferrous metal (75.7%),
aluminum scrap (71.2%), and aluminum cans (59.4%) are currently being recycled at the
highest levels. Although corrugated & kraft paper is the largest component by weight of
the potentially recyclable waste stream, only 20.4% is currently being recycled.
CDM Camp Dresser & McKee
5-1
I
I
I
Potential Recvclables
Corrugated & Kraft Paper
Leaves I Other Yard Waste
Food Waste
Other Paper
Newsprint
Ferrous Metal
Textiles, Rubber, & Leather
Clean Wood
Other Plastic
Tin-Steel & Bimetal Cans
Magazines
Aluminum Scrap
Aluminum Cans
Clear Glass Containers
High-Grade Paper
Grass Clippings
Other Plastic Containers
Other Non-Ferrous Metal
Brown Glass Containe)"s
Colored.HDPE Containers
Clear HDPE Containers
PET Bottles
Green Glass Containers
Other Glass
TOTAL
I
I
I
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I
I
I
I
I
I
I
I
I
I
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SMRYSORTXLS - POTENTIAL RECYCLE
Table 5-1
Current Recycling Levels of the Residential and Commercial Waste Streams
Residential
"Cl
" "
~-; on
'"
e :: c
.. c c
tl = 0
rol<E-
2,351
5,205
2,436
2,603
1,671
124
915
629
603
583
671
55
151
379
185
238
241
49
104
167
153
87
39
3
19,641
Commercial
"Cl
<II "
~-; on
'"
e :: c
.. c c
1il c 0
rol<E-
2,932
420
2,393
2,069
440
342
696
708
624
298
78
151
124
147
313
211
120
196
186
126
70
72
19
65
12,800
ResidentiaU Commercial
:;.
'"
Q
] <II
'" on
e ~
~ g
rolE-
14.47
15.41
al "
cu-;~
e :: c
~ 2 S
rol<E-
5,283
5,625
4,829
4,672
2,111
466
13.23
12.80
5.78
1.28
4.41
3.66
3.36
2.41
2.05
0.57
0.75
1.44
1.36
1.23
0.99
0.67
0.80
0.80
0.61
0.43
0.16
0.19
88.88
Other
Concrete 0 116 116 0.32
A.sphalt 0 0 0 0.00
Polyethylene Film 858 1,070 1,928 5.28
ines 2,059 815 2,875 7.88
Car Batteries 0 0 0 0.00
Other 758 516 1,274 3.49
Gypsum Board & Plaster 49 261 309 0.85
White Goods 0 4 4 0.01
Roofing Materials 298 228 527 1.44
Polystyrene Foam 203 172 374 1.03
Disposable Diapers 706 163 870 2.38
Treated Lumber 0 59 59 0.16
Batteries 27 51 79 0.22
Tires 0 0 0 0.00
Metal 121 18 139 0.38
Blocks 0 4 4 0.01
Bricks 6 4 10 0.03
TOTAL 5,086 3,481 8,567 23.47
1,611
1,336
1,227
881
750
206
275
527
498
449
361
245
290
293
222
158
58
68
32,442
Recycled
"Cl
" "
~-; on
'"
e :: c
.. c c
"t; = Q
rol<E-
1,357
0
0
30
410
1,450
0
0
0
30
15
510
402
36
12
0
0
95
15
7
28
21
12
0
4,430
Cii
'0
E-
"Cl
" <II
=c; on
'"
e :: c
.. c c
'f;; c 0
rol<E-
6,640
5,625
4,829
4,702
2,521
1,916
1,611
1,336
1,227
911
765
716
677
563
510
449
361
340
305
300
250
179
70
68
36,872
Combined
>>
c~]
" " C,I
C,I ... >>
... ... C,I
" :: "
p.UI:l:
20.4%
0.0%
0.0%
0.6%
16.3%
75.7%
0.0%
0.0%
0.0%
3.3%
2.0%
71.2%
59.4%
6.4%
2.4%
0.0%
0.0%
27.9%
4.9%
2.3%
11.2%
11.7%
17.2%
0.0%
12.0%
10,000 10,116 98.9%
7,000 7,000 100.0%
9 1,937 0.5%
0 2,875 0.0%
779 779 100.0%
0 1,274 0.0%
0 309 0.0%
232 236 98.4%
0 527 0.0%
2 376 0.5%
0 870 0.0%
0 59 0.0%
0 79 0.0%
19 19 100.0%
0 139 0.0%
0 4 0.0%
0 10 0.0%
18,041 26,608 67.8%
8121/97
I
'"
~
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--< Tons
'"
0 N w ~ Ul 0\ -.l
~ 0 0 0 '0 '0 '0 0
>< 0 0 0 0 0 0 0
r 0 0 0 0 0 0 0 0
I '"
-0
0 Corrugated & Krall Paper
@
Z
I ..,
:; Leaves / Other Yard Waste
r
:<l
tT1
() Food Waste
--<
I ()
r
tT1
Cl Other Paper
:<l
>-
-0
I ::c Newsprint
Ferrous Metal
I ~tiles, Rubber, & Leather ~
0
....
(tl
::I
Clean Wood ....
I ,...
~
-
I Other Plastic ~
(tl
~
<<
I -
Tin-Steel & Bimetal Cans ~
- ~
(tl
~ ,...
Magazines l1Q
==
I ~ ~
....
(tl (tl
Aluminum Scrap ~ VI
,...
~ I
- l-'
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Aluminum Cans :I
1JJ
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Clear Glass Containers ,...
:I
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==
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I <<
I III
::: ~
VJ~
e:,.cc
_, ::1,
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nn
o .::
Colored HDPE Containers .:: ::!
::3 cc
.... :::
'-<: :::.
I '-<
Clear HDPE Containers :;0
cc
0
'-<:
PET Bottles 0
~
I 0-
Green Glass Containers
00
I ---
N Other Glass
....
---
\0 ~__w
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5.2 Recommendations
. In an effort to divert waste from the City of Salina MSWLF, the City should continue the
evaluation of its leaf and grass/yard waste composting pilot program.
. The City and County should educate the commercial and industrial sectors about the
advantages of recycling corrugated cardboard and promote similar recycling efforts
throughout the County.
. The City of Salina should review other methods of diverting yard waste from the
MSWLF, such as additional yard waste drop-off events throughout the year.
. The City and County should work with the industrial sector to investigate disposal
alternatives for the large food waste component.
. Additional investigation of the construction and demolition waste stream is urged to
ensure the proper handling and disposal of those items not entering the City of Salina
MSWLF.
. The City and County should consider the use of the data developed in this study to
evaluate future KDHE Venture Grant Applications dealing with waste diversion and
recycling projects.
CDM Camp Dresser & McKee
5-4
'7
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City of Salina
Solid Waste Characterization Study W orkplan
November 1996
Prepared for:
City of Salina, "f(ansas
Prepared by:
Camp Dresser & McKee Inc.
250 North Kansas, Suite 110
Wichita, Kansas 67214
CDM Project No: 8558-20193
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Table of Contents
1.0 INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 1-1
1.1 Purpose of Report ................................................... 1-1
1.2 Scope of Work. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 1-1
1.3 Report Structure .............;..................................... .1-2
2.0 WASTE GENERATION AND COLLECTION PRACTICES .................. 2-1
2.1 Waste Generation Rates. .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 2-1
2.2 Waste Collection Practices. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 2-1
2.3 Sources to be Sampled. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . 2-3
3.0 COMPOSITION SAMPLING EVENTS ................................... 3-1
3.1 Design of Sampling Program ........................................... 3-1
3.2 Sampling Method. . . . . . . . . . . . . . . . . . . . . . . . . . . . . , . . . . . . . . . . . . . . . . . . . . . . 3-1
3.3 Accepting/Rejecting Samples. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-2
3.4 Sorting Procedures .................................................. 3-2
3.5 Safety ............................................................. 3-6
4.0 FINDINGS PRESENTATION........................................... 4-1
4.1 Field Data Logs . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-1
4.2 Statistical Analysis of Data. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-1
APPENDIX A - FIELD INFORMATION FORMS
APPENDIX B - HEALTH & SAFETY PLAN
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2-1 Breakdown of Monthly Waste Quantities by Material Type
2-2 Saline County Hauling Companies
List of Tables
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Section 1
Introduction
The City of Salina and Saline County are in the process of updating the county's solid waste
management plan. One overall goal of the plan is to reduce the volume of waste that requires
disposal by landfilling through the development of waste reduction programs. In order to
efficiently design waste reduction programs and disposal facilities, however, it is important to
first assess the characteristics of the waste that will be managed in the programs. Solid waste is
not only complex in its composition, but varies with geographic location, source, season, and
social and economic conditions of its generators. To assess the characteristics of the county's
residential, commercial and industrial, and construction/ demolition waste, the City of Salina has
contracted with Camp Dresser & McKee Inc. (CDM) to conduct a characterization study of this
waste stream. This workplan is a description of CDM's approach to conducting the study.
1.1 Purpose of Report
The purpose of this waste characterization study is to provide data to the City of Salina and
Saline County for use in the design of comprehensive programs for overall waste management,
including source reduction, reuse, recycling, composting, and disposal. The following data are
required to accomplish these ends:
. identification of the distribution by generator of selected waste stream components
by weight percentages;
. identification of the quantities of landscape waste, construction and demolition
waste, and other anomalous materials in the waste stream.
Examples of the use of this data include: determining what types of materials will be targeted for
source reduction efforts; and determining what impacts of these efforts will have on the total
waste stream. The data could also be used in determining facility sizes and specific facility
equipment needs such as sizes of balers for a recycling facility or windrow turners for a
landscape waste compo sting facility, and size and financial impacts on landfills resulting from
waste reduction programs.
1.2 Scope of Work.
The following tasks will be conducted to achieve the goals of the study:
. Design of waste ,characterization program including identification of waste
generators;
. Performance of three sampling events over four seasons (sampling refers to the
selection of specific samples of waste from within vehicles selected for sampling:
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Section 1
Introduction
sorting refers to the separation of waste samples obtained from the selected
vehicles) ;
. Visual characterization of bulky, landscape, and construction/ demolition, industrial
waste;
. Preparation of interim report of findings after the fall and winter sampling events;
and
. Preparation of final study report.
1.3 Report Structure
This document will discuss the following information:
. Waste Generation and Collection Practices (Section 2)
. Composition Sampling Events (Section 3)
. Findings Presentation (Section 4)
. Health & Safety Plan (Appendix A)
. Field Information Forms (Appendix B)
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Section 2
Waste Generation & Collection Practices
2.1 Waste Generation Rates
A preliminary investigation has been conducted by CDM in order to determine the quantity of waste
being generated within Salin~ County. The City of Salina Municipal Solid Waste Landfill (MSWLF)
tipping records from Fiscal Year 1995 were used to develop this information. CDM will augment
,and clarify this information prior to the first draft interim report. A summary of the initial results are
provided in Table 2-1.
Table 2-1
Breakdown of Monthly Waste Quantities by Material Type
Type of October 1995 November 1995 December 1995
Waste Tons % Tons % Tons %
Residential 2,245 31.1% 2,046 30.6% 1,857 31.8%
Concrete 46 0.6% 18 0.3% 5 0.1%
Landscape 165 2.3% 81 1.2% 25 0.4%
Commercial 1,449 20.1% 1,363 20.4% 1,277 21.9%
Industrial 2,334 32.4% 2,243 33.6% 2,042 35.0%
Construction 930 12.9% 911 13.6% 614 10.5%
Medical 4 0.1% 4 0.1% 2 0.0%
White Metal 19 0.3% 14 0.2% 9 0.2%
Agricultural, 21 0.3% 0 0.0% 5 0.1%
Total 7,213 6,680 5,836
I , Saline County Waste Breakdown (Fall 1995) I
Residential - 31.2% Industrial- 33.6%
Commercial - 20.8% Construction - 12.4%
2.2 Waste Collection Practices
CDM's first task in determining the composition of waste generated in Saline County is developing a
mass balance of the waste flow in the county. The mass balance is used to determine the sources of
waste materials and thus, determine which sources of materials should be sampled to develop a
complete cross section of the waste stream composition. The information to be collected includes
waste generators/ collectors, number of trucks, collection service areas, waste quantities, currently
recycled quantities by type, etc. The mass balance is developed through an audit of the generators
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Section 2
Waste Generation & Collection Practices
and collectors. The list of haulers was compiled from landfill records and CDM's knowledge of
waste management practices in the county (see Table 2-2).
Table 2-2
Saline County Hauling Companies
Hauler Phone Number of Collection Service Area
Number Trucks
City of Salina (913) 826-7375 9 Rear Loaders Residential - Salina
Salina Waste 3 Rear Loaders Residential- Salina & Townships
System, Inc. (913) 825-9155 3 Front Loaders Commercial - Salina & Townships
3 Roll-Offs Industrial- Salina & Townships
Recycle It, Ine. (800) 324-8020 5 Roll-Offs Commercial- Salina & Townships
Industrial- Salina & Townships
Refuse & (913) 823-6137 3 Rear Loaders Residential- Salina & Townships
Recycle Commercial- Salina & Townships
Peterson Refuse (913) 225-6704 1 Rear Loader Residential- Salina & Townships
Commercial - Salina
Gimenson (913) 536-4277 2 Rear Loaders Residential- Townships
Commercial- Townships
Harris Trash (913) 823-3996 1 Rear Loader Residential- Salina
Recycling, Inc. 1 Roll-Off Commercial - Salina
The objective of the audit is to assure the waste sorted by the CDM crew accurately represents the
characteristics of the generators in the city and county. This is to assure the waste chosen for sorting
does not come from only one part of the county or from only one waste stream. To provide this
assurance, the quantities of Waste generated in the county (by material type), the geographical
distribution of waste generation, the collection routes of the haulers (both public and private), and
the current levels of recycling must be established.
Based on discussions with the identified haulers, CDM determined the individual companies'
hauling routes and service areas as shown in Table 2-2 and depicted in Figure 2-1. For the most part,
Salina's residential waste is collected by the City of Salina Department of General Services (about
75%) and Salina Waste (about 20%), with a small portion being collected by Refuse and Recycle
(about 5%). This is the extent of the City's waste hauling operations, hauling only within Salina city
limits and only from resident~al houses and apartment buildings with 3 or less units.
The residential hauling routes for both the City's trucks and Salina Waste are the same (as shown in
Figure 2-1) in order to decrease confusion to customers with separate pick up days. The Monday and
Tuesday routes (southern Salina) consist of typically middle income families. The Wednesday route
(near southwest Salina) is mostly lowto middle income families. The Thursday route (north and east
Salina) has middle to high income families typically in eastern Salina and low income families living
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Section 2
Waste Generation & Collection Practices
to the north. The Friday route (western Salina) is mainly low to middle income families with a
significant portion of these customers being elderly and/ or renters.
Commercial and industrial waste collection throughout the County, as well as residential waste
outside the City of Salina, is performed solely by private hauling companies. Salina Waste and
Refuse & Recycle collect the majority of the smaller commercial stops in Salina, while Salina Waste
and Recycle It handle most of the larger commercial and industrial collections throughout the
county. Much of the waste generated in the townships of Saline County (outside Salina) is collected
by smaller hauling companies.
Waste collected in the county is typically disposed at the Salina MSWLF. Any truck that has
mechanized tipping capabilities brings its waste directly to the active disposal area at the landfill.
Other trucks may dispose their refuse at one of four 30 cubic yard containers in the convenience area
located adjacent the scale house. This area typically receives large quantities of landscaping and
construction/ demolition material.
2.3 Sources to be Sampled
The source of the samples will be determined based on results of the waste audit. COM identified
which collection routes will be sampled. However, we will maintain the flexibility to adjust the
sources based on field observations and discussions with haulers as the material is delivered. As the
trucks enter the city landfill, a solid waste professional from COM will identify the trucks to be
sampled as well as provide direction to the scale operator. COM may interview the driver to assure
the source of the materials is correct. COM will then identify the sample from within the delivered
load and direct staff to collect the material and initiate sampling. The person who identifies the
samples is referred to in this protocol as the "sample collector."
The quantities and composition of other materials such as sludges and petroleum products will be
determined through interviews with haulers and generators. This material cannot be sampled as we
assume the material is delivered erratically.
Standard procedure for determining the number of samples to be collected during a waste stream
characterization study involves apportioning the total number of samples to be collected in the study
to the waste stream portions by their respective percentages of the whole. For example, if 100
samples were to be collected during a study and the waste stream being sampled consisted of 70
percent residential waste and 30 percent commercial and institutional waste, then 70 samples would
be collected from the residential waste stream and 30 samples would be collected from the
commercial and institutional portion. The number of samples required to provide an accurate
estimate for the study area is dependent on the size and characteristics of the study area. For this
study, 40 to 50 samples each a.re to be collected during each of the 5-day sorting events. The sorting
events will be conducted during three seasons (fall, winter, spring/summer).
The annual volumes of the various waste streams estimated in Section 2.1 from the Salina MSWLF
records were used to apportion the number of samples to be collected in this study. Data showed
approximately a 3:2 ratio of residential to commercial waste for Saline County. Therefore, COM will
sample 24 to 30 residential and 16to 20 commercial trucks during each of the sorting events. The city
residential samples will be taken primarily from City and Salina Waste trucks during all days of the
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Section 2
Waste Generation & Collection Practices
week so that all levels of income housing is sampled. Since there are small quantities of refuse being
generated in the townships, generally all township collection routes will be sampled.
Most of the commercial waste to be sampled will be from front and rear loading collection vehicles
which collect waste from multiple smaller commercial businesses. The larger commercial customers
using large capacity roll-off containers will typically not be sampled so that the results will not be
skewed from one load. However, these loads will be visually examined during tipping on the landfill
in order to determine an approximate volume percentage of materials. This visual estimation
procedure will also be done for all industrial loads, which are most commonly from Tony's Pizza
(typically unmanageable food waste) and Philip's Lighting (typically broken florescent tube glass).
Field observations and waste sort data for commercial and industrial businesses will be verified by
information obtained from the county-wide waste audit. Interviews with generators and area
recycling facilities will provide a current assessment of recycling and disposal activities affecting the
quantity and type of waste being landfilled.
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Section 3
Composition Sampling Events
(Note: For the purpose of this document the term "sampling" refers to the selection of specific samples of
waste from within vehicles selected for sampling. The term "sorting" refers to the separation of waste samples
obtained from the selected vehicles.)
3.1 Design of Sampling Program
Waste characterization field work will be performed over three seasons; Fall, Winter, and
Spring/Summer. The length of each sort will be based on the results of the waste audit and the data
developed during the sort, but will typically proceed for five days, Monday through Friday. Field
work will not be scheduled for any period that includes a day on which waste is not collected be-
cause of a holiday or other special event.
Sampling and sorting, if possible, will be conducted in areas that can be set aside at the Salina
landfill. It is preferable to have a paved or other controlled surface.
The selection of the specific solid waste samples is based on the random sampling of pre-determined
loads from selected collection routes (see Section 2.3 for a discussion of vehicle route selection
procedures). Although materials disposed of in the landfill's convenience area will not be sorted,
CDM will periodically monitor these containers throughout the sampling events to insure an
accurate visual estimation of these bulky materials.
All loads entering the Salina MSWLF will be surveyed by use of a standardized check sheet (see
"Gate Form" in Appendix A) which is to be completed by the scale house employee or CDM sample
collector.
3.2 Sampling Method
The selected solid waste collection vehicle will dump its load at the usual tipping area on the landfill.
The following procedure will be followed to obtain the sample to be sorted.
CDM's on-site staff supervisor shall use a grid selection technique to select a sampling point from the
total truck load. The grid selection technique involves either physically or conceptually dividing the
total load into a number of grids. Throughout the sampling event, samples to be sorted are selected
from each of the different grids. The grids are designed to provide an initial, random sampling point,
not a cube of refuse. Refuse can be collected from any area in the selected grid, provided the grid .
represents the primary target. This method is intended to keep the crew from avoiding certain
unusual (for example, cardboard and tree trimmings) or unappealing items in the refuse.
The CDM supervisor will instruct the front-end loader operator or alternate on where to obtain the
sample. The target sample size will be approximately 200 pounds to 250 pounds (approximately a 4-
foot by 4-foot by 2-foot load). The sample is brought to the sorting area and dumped in a designated
area. Because the area at Salina Landfill on which the sample is to be deposited is not paved, the sort
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Section 3
Composition Sampling Events
area is to be prepared by placing a cloth tarp on a level surface near the working area. The sheet will
be surrounded and held down by sandbags or the containers that will be used for sorting.
Some items in the sampled loads of waste will be too large to be included in the samples. In
addition, the samples may not adequately represent concentrations of a single material, such as
corrugated cardboard, within the sampled load. To provide a basis for making appropriate ad-
justments in the results of the sorting, any bulky items or concentrations of a single material will be
described on the "Data Form for Waste Samples."
3.3 Accepting/Rejecting Samples
The supervisor will have the responsibility for accepting or rejecting loads for sorting. Reasons for
rejecting loads include, but are not limited to, the following:
. Unidentifiable contents,
. Hazardous waste or materials posing a safety hazard,
. Hospital waste, and
. Materials soaked in a liquid other than rain or water.
If such a load is identified, it will be reported to the facility manager for removal from the sampling
area.
3.4 Sorting Procedures
When the sorting takes place, the sorted materials will be placed into labeled containers. Some
preparation of these containers is necessary prior to beginning the sort. The sort containers should
be weighed empty to obtain a tare weight. The containers should be labeled or numbered and the
tare weight clearly marked on each container. The tare weight corresponding to each container label
or number should be recorded for future reference. The tare weights should be checked periodically.
The containers should remain as free from extraneous debris such as mud, ice, and snow, as possible
to avoid changes in the tare weight. It may be necessary to periodically clean the containers.
Prior to manually sorting waste or transferring waste to a sorting table, the waste should be spread
apart in the area it is deposited. Visual observation of the waste prior to manually sorting is critical
to worker safety. The potential for cuts, scrapes, and puncture wounds exists if workers grab arm-
loads of waste or stick hands deeply into waste. All unopened bags of waste will be opened using
care not to be cut or scrapped. Bags will be broken open using shovels or similar long handled tools.
The sample should be transferred to the sorting table using a shovel and further spread out using
hand-held tools to allow a visual observation of its contents.
The sorting table is constructed by placing 4-foot by 8-foot sheets of plywood across sawhorses
apprmdmately 3-foot high. The table is covered with plastic sheeting to simplify collection of the
fines. Sorting will be done primarily at the sorting table into 5-gallon buckets which, when full, are
emptied into the polycart containers at the perimeter of the sort area. Each sample of waste will be
sorted by hand into 38 categories (listed at the end of this section). Items of special interest such as
batteries, paints, and hazardous chemicals will be handled separately.
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Section 3
Composition Sampling Events
Regularly, the sort supervisors will check the containers into which waste is being sorted to ensure
that the sorting is being performed properly. Sorting will continue until only a few pounds of the
smallest pieces from the sample remain on the screen. Care will be taken to sort small pieces of
broken glass and ceramic into their appropriate categories. If a significant number of ferrous metal
items such as bottle caps rema:in on the screen, they will be removed by passing a large magnet back
and forth just above the screen.
Because food waste is by far the most difficult of the sample categories to sort, the sorting team will
use the same container for food waste during the entire study. As food residue builds up on these
containers, the tare weight used in calculating the net weight of the food waste will be adjusted.
When the sorting of one sample is completed, the filled containers are weighed and the gross weights
recorded. Comments on the characteristics of the material may need to be recorded following visual
analysis. After each container is weighed, the sorters will dump its contents into a rear loading
disposal truck or in an area where the front-end loader can pick them up and return them to the
landfill for disposal. The sampling/ sorting cycle continues until the daily sampling quota is
completed.
The following are the proposed sort categories of waste:
Newsprint. Anything printed on newsprint, including advertising inserts found with newspapers in
the trash. Advertising inserts found separate from newspapers will be classified as "other paper."
Corrugated cardboard and kraft paper. All cardboard made of brown or yellow-brown paper and
containing corrugations, and all heavy brown paper of the type used to construct corrugated
cardboard (primarily grocery bags).
High-grade paper. White and . colored uncoated bond paper and computer printout paper. Includes
canceled checks. Does not include envelopes, carbon paper, or paper used in multi-copy carbonless
forms (sometimes called "NCR forms").
Magazines. All periodicals and catalogs bound in soft covers except those printed on newsprint or
included in newspapers and found with newspaper in the trash.
Other paper. All paper products other than newspaper, corrugated cardboard, kraft paper,
high-grade paper and magazines. Includes milk cartons, boxboard (including boxboard containers
with metal bottoms) and other types of paper packaging, paper towels and tissues, "junk" mail,
advertising inserts not found with newspapers, and a large number of other items.
PET (polyethylene terephthalate) bottles. Clear and green plastic carbonated soft drink bottles, and
other plastic bottles if identifihble as PET -based on labeling or a mold-mark in the center of the
bottom of the container.
Clear HOPE (high-density polyethylene) containers. Translucent plastic milk, water and juice con-
tainers, and certain personal hygiene products.
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Section 3
Composition Sampling Events
Colored HOPE (high-density polyethylene) containers. Pigmented (wl)ite or colored) HDPE
containers for beverages, cleaning products such as detergents, cleaning products, and certain per-
sonal hygiene products. Does hot include 5-gallon buckets.
Other plastic containers. Includes all small containers composed of rigid (non-film, non-foam)
polyvinyl chloride (#3), low-density polyethylene (LDPE--#4), polypropylene (#5), and polystyrene
(#6). Includes containers in the form of bottles, trays, and tubs. Includes PET containers other than
bottles (e.g., trays). Does not include anything composed of polystyrene foam.
Polyethylene film. All polyethylene bags, plus other relatively large pieces of polyethylene film.
Includes both LDPE and HDPE bags. Includes garbage bags, and similar plastic bags used in retail
stores. Includes newspaper delivery bags, and the type of plastic covering used by retailers. Does not
include plastic film used as a wrapping material or as part of a package containing paper or
Styrofoam.
Polystyrene foam. Cups, plates, take-out food containers, etc. Primarily used by the food service
industry.
Other plastic. All plastic other than PET bottles, HDPE containers, other plastic containers, and
polyethylene film as defined above.
Food waste. All items produced or gathered for use as food, including the inedible portions. In prac-
tice, some food waste becomes part of the fines category. Food waste includes coffee grounds, but the
majority of coffee grounds are' found in the fines category. Includes contents of food and beverage
containers found in the waste samples.
Grass clippings. Pieces of grass cut from lawns. Does not include grass pulled up by the roots or
otherwise stripped from a lawn.
Leaves/Other yard waste. Leaves, shrub and garden trimmings, weeds and wild grasses, pine nee-
dles and cones, tree branches and twigs, vegetative ground litter, and associated dirt. Also includes
grass pulled up by the roots or otherwise stripped from a lawn.
Wood. Includes all wood other thim "natural" wood such as tree branches. Includes both lumber and
reconstituted wood such as plywood, particle board, composition board, chip board, and some
ceiling tile. Also includes sawliust, wood shavings, cork, and wicker.
Treated lumber. Wood that is chemically treated (e.g., creosote-treated timbers and pressure-treated
lumber), painted or otherwise, finished, covered with plastic laminate, or laminated with other
materials (e.g., some indoor paneling). Does not include plywood or composition board heavily
coated with tar for use as a roof covering.
Textiles, rubber, and leather. Allfabrics, rubber, and leather. Includes clothing of all kinds, including
composite clothing such as sn~akers and plastic clothing such as vinyl raincoats, belts and shoes.
Includes handbags and purses. Includes foam rubber, as well as pillows and cushions filled with
fibers or foam rubber. Includes carpeting, carpet padding, and rugs. Includes fabrics found in
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Section 3
Composition Sampling Events
bedding, towels and washcloths, cloth napkins and place mats, curtains and drapes, awnings,
furniture, tents, tarpaulins, and umbrellas. Includes tires, rubber hose, and surgical gloves.
Disposable diapers. All single-use diapers and their contents. Includes both infant and adult diapers,
but does not include absorbent bed pads.
Fines. Materials that pass through the half-inch mesh screen on the bottom of the sorting box, and
items that do not pass through the screen but are too small to sort efficiently. The largest components
of the material that passes through the screen are coffee grounds, small bits of food, and cat litter.
Other components include dust, cigarette butts, ashes. The primary components of the fine material
that does not pass through the screen are small pieces of food and "other paper."
Aluminum cans. All-aluminum food and beverage cans. Includes soda and beer cans, as well as the
type of small aluminum can. Does not include aluminum aerosol spray cans.
Aluminum scrap. Aluminum sheet and rigid aluminum. Includes aluminum folding chairs, siding and
flashing, Venetian blinds, thresholds and weather stripping, and similar items. Major components
are aluminum foil, and similar items. Also includes aluminum aerosol spray cans.
Other nonferrous metal. All metal other than iron, steel, and aluminum. Includes copper, brass, lead,
zinc, bronze, and tin (but not "tin" cans). Includes circuit boards, solder, and electrical wire in which
the metal appears to weigh more than the non-metal components. Does not include any batteries.
Tin-steel and bimetal cans. Food and beverage cans with steel sides, whether or not plated with tin,
and other steel cans having any of the structures typical of steel food and beverage cans. Also
includes the tops of these cans. Includes cans with steel sides and aluminum tops. Does not include
paint cans, aerosol spray cans, or the type of can in which paint thinner is generally sold. Weight
includes food residue on the surface of the cans (cans will be emptied before weighing, but not
washed out).
Ferrous metal. All iron-based objects other than tin-steel and bimetal cans as defined above. Includes
steel trash cans, steel furniture, wire hangers, the steel parts of electrical and electronic devices, and a
large number of other items. Includes paint cans, steel aerosol spray cans, and the type of can in
which paint thinner is typically sold.
Batteries. All batteries other than vehicle batteries and large industrial-type batteries. Includes
alkaline, zinc-carbon, nickel-cadmium, lithium, silver oxide, and mercuric oxide batteries, as well as
additional types.
Glass containers (general). Glass food and beverage containers and other containers made from the
same type of glass. Does not include ceramics, drinking glasses, glass plates, cooking utensils, ash
trays, perfume bottles, or containers for cosmetic products. Includes caps left on empty containers by
the consumer. Weight includes food residue on the surface of the glass (containers will be emptied
before weighing, but not washed out). "Glass containers" are not a category for this study; this
definition is included to clarify the definitions of clear glass containers, brown glass containers, green
glass containers, and" other noncombustibles."
CDM Camp Dresser & McKee
3-5
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Section 3
Composition Sampling Events
Clear glass containers. Glass containers with no color or tint in the glass.
Brown glass containers. Glass containers with brown or amber color or tint in the glass, however
faint.
Green glass containers. Glass containers with green or emerald color or tint in the glass, however
faint.
Other combustibles/noncombustibles. All items that do not fall within the definitions of any of the
other categories. Includes absorbent pads used in health care, tampons and sanitary napkins, animal
feces unless mixed with cat litter, oils, flower arrangements, tar paper, roofing shingles, and vinyl-
asbestos floor coverings. Also includes composite items. All furniture not included in the metal
category, including mattresses and box springs. Includes contained dirt, gypsum board and plaster,
masonry materials, ceramics, non-beverage aqueous solutions, and fiberglass insulation. Includes
glass that does not fall within the definition of "glass containers" above, such as window glass, glass
cosmetic containers, decorative glass, and light bulbs. Also includes glass containers other than clear,
brown, and green containers.
Roofing materials. All roof covering materials that do not fall within one of the other categories.
Includes asphalt roofing shingles and roofing felt (often called tar paper). Also includes plywood and
any kind of composition board if coated with tar for use as a roof covering.
Metal. All ferrous and nonferrous metal items including all-metal furniture such as filing cabinets.
Poured concrete. All concrete except concrete blocks.
Bricks. Bricks and associated mortar.
Blocks. Concrete blocks, cinder blocks, cement blocks, and associated mortar.
Gypsum board and plaster. Includes loose plaster and gypsum-based wallboard commonly referred
to by the trade names "sheetrock" or "drywall."
White Goods. Large appliances not categorized as metals.
Other items such as sludges, medical wastes, non-defined institutional wastes, animal wastes and
petroleum product wastes wilhbe identified through interviews with generators and haulers. This
material cannot be sorted at the disposal facility.
3.5 Safety
The approved COM Solid Waste Characterization Health and Safety Plan (see Appendix B) will be
followed during the solid waste sampling and sorting event. A copy of the plan should be carefully
reviewed by all participants prior to beginning any sampling and sorting activities. The plan should
be reviewed with the landfill supervisor for coordination of safety procedures on-site.
A training session will be conducted before initiating fieldwork. The session will stress the
procedures discussed in this report as well as the requirements set forth in the Solid Waste
CDM Camp Dresser & McKee
3-6
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Section 3
Composition Sampling Events
Characterization Health and Safety Plan. The field staff will follow the safety procedures during the
waste composition sampling.
The sorting crew will, at a minimum, consist of a supervisor from CDM who is experienced in sorting
and two assistant sorters. The supervisor will record data, instruct sorters on material identification,
and discuss sample selection methods with operators and haulers.
The supervisor will distribute gloves, safety helmets, safety goggles, dust masks, and other personal
safety equipment to each crew member. The supervisor will be responsible for ensuring that all
safety equipment as described in the Solid Waste Characterization Health and Safety Plan is at the
site and that the Plan is followed.
CDM Camp Dresser & McKee
3-7
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Section 4
Findings Presentation
4.1 Field Data Logs
When sorting and collection of the fines are complete, the sorters will bring the containers to the
weighing area. As each container is placed on the scale, the sort supervisor will look into the
container to see which category of waste is in the container and to check for items that do not belong
to that category. If the material in the container is satisfactory, the sort supervisor will read the gross
weight of the container and contents and record it in the appropriate spot on the "Data Form for
Waste Samples" (se,e Appendix A) supplied for that sample by the sample collector.
4.2 Statistical Analysis of Data
The weight data collected for each material in each sample are used to calculate percentages of the
materials by weight in relation to the total weight of each sample. The percentage data for each
material per sample will be used to calculate mean material percentages in relation to the respective
waste streams being sampled
For each sampling event composition data set, and for the cumulative three-season data set, the
mean will be developed for each material category. This identifies the percent of that particular
material type within the county's waste stream. The standard deviation from the sample mean and
90-percent confidence intervals will also be calculated for each material category. The standard de-
viation from the sample mean for each material type will be calculated to assess the variability of the
samples. A higher standard deviation value indicates greater variation in the data.
The 90-percent confidence interval for the percentage of each material in the waste stream is cal-
culated to provide a range of percentages for each material that could be expected to contain the
actual mean percentage of the material during the sampling event with a 90-percent statistical
probability. The confidence interval is assumed to be accurate in the absence of sampling and
sorting errors and with the assumption that the results for the individual samples are normally
distributed. This assumption of normal composition is generally reasonable.
It can be expected that material categories with the largest confidence intervals in proportion to
their percentage in the samples are categories such as high-grade paper and other landscape waste,
which are generally concentr~ted in a relatively few number of samples. Conversely, waste
categories with the smallest confidence intervals in proportion to their percentage in the samples are
categories such as other recyclable paper and food waste, which are generally found in significant
quantities in nearly all samples.
CDM Camp Dresser & McKee
4-1
GATE FORM
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AM / PM
Time:
Date:
Hauler:
o City of Salina
Type of Vehicle:
o Rear Loader
Landfill Routing:
Tonnage:
Hauling Location:
o Salina (City) 0 Township (Check all below)
OAssaria 0 Bavaria 0 Bridgeport 0 Brookville 0 Falun
o Hedville 0 Kipp 0 Mentor 0 New Cambria 0 Smolan
Type of Waste (Check all that apply):
o Residential 0 Commercial
o ConstructionlDemolition (Describe)
o Other
o Refuse & Recycle
o Recycle It
o Salina Waste
o Pick Up
ODrop Off Boxes
o Semi
o Roll-Off
o Front Loader
o Landfill
tons
o Out of County
o Glendale 0 Gypsum
o Other
o Other
o fudustrial
o Landscape
Hauler:
o City of Salina
Type of Vehicle:
o Rear Loader
Landfill Routing:
Tonnage:
Hauling Location:
o Salina (City) 0 Township (Check all below)
OAssarhl 0 Bavaria 0 Bridgeport 0 Brookville 0 Falun
o Hedville - 0 Kipp 0 Mentor 0 New Cambria 0 Smolan
Type of Waste (Check all that apply):
o Residential 0 Commercial
o ConstructionlDemolition (Describe)
o Refuse & Recycle.
o Other
o Recycle It
o Salina Waste
o Pick Up
ODrop Off Boxes
o Semi
o Roll-Off
o Front Loader
o Landfill
tons
o Out of County
o Glendale 0 Gypsum
o Other
o fudustrial
o Landscape
o Other
GATEFORM.WPD
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Sample No.
Source:
Hauler:
Sector: 0 Residential
DATA FORM FOR WASTE SAMPLES
Date: Time:
amlpm
Weather:
Vehicle:
o Commercial 0 Industrial 0 Landscape 0 Construction/Demolition
NET WEIGHT OF MATERIAL COMPONENT
Newsprint Cardboard & Kraft Paper
High-Grade Paper Magazines
Other Paper PET Bottles
Clear HDPE Containers Colored HDPE Containers
Other Plastic Containers Polyethylene Film
Polystyrene Foam Other Plastic
Food Waste Grass Clippings
Leaves / Other Yard Waste Clean Wood
Treated Lumber Textiles, Rubber, & Leather
Disposable Diapers Fines
Aluminum Cans Aluminum Scrap
Other Non-Ferrous Metal Tin-Steel & Bimetal Cans
Ferrous Metal Batteries
General Glass Containers Clear Glass Containers
Brown Glass Containers Green Glass Containers
Other Roofmg Materials
Metal Poured Concrete
Bricks Blocks
Gypsum Board & Plaster White Goods
Unsampled Materials in Load or Additional Notes:
RAWDATA.WPD
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RELEASE FORM
I, .' hereby release and hold harmless Camp Dresser & McKee Inc.
(CDM) and its officers, directors, employees, subcontractors, and consultants from any and all claims, causes
of action, or liability associated with the work that I am undertaking on behalf of the CITY OF SALINA.
Print Name
Signature
Date
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HEALTH AND SAFETY PLAN
FIELD SAMPLING
SOLID WASTE CHARACTERIZATION ANALYSIS
Camp Dresser & McKee, Inc.
EMERGENCY CONTACT: Chris Marlowe
(908) 225-7042 ext 332
(800) 313-5593 (24 Hour)
Raritan Plaza One
Edison, NJ 08818
(908) 225-7000
1. A copy of this Health and Safety Plan must be kept on site during the entire sampling event.
2. All Field Sampling staff must complete two copies of the emergency contact form, Appendix A to this
Plan. One copy of the emergency contact form for each staff person must be attached to this Plan and kept
on site during the entire sampling event. The second copy of the form must be left with the CDM
emergency contact staff at the local CDM office.
3. The following information, for each sampling site, must be completed prior to beginning the sampling
event.
Name of Landfill or Sampling Site:
Dates at Site:
Fire Phone Number:
Ambulance Phone Number:
Police Phone Number:
Salina Municipal Solid Waste Landfill
11/11/96 to 11/15/96, 2/17/97 to 2/21/97
911 or 826-7340
823-3862 (TAC-EMS)
911 or 826-7210
Nearest Hospital with Emergency Facility
Name:
Hospital Phone:
Hospital Address:
Contact Name:
Directions from site to Hospital:
Salina Regional Health Center
452-7000
400 S. Santa Fe, Salina, Kansas
Diana Knudson
North on Burma Road to Crawford Street,
Go right (east) to Santa Fe Avenue,
Go left (north) to Hospital (on the left)
SEE ATTACHED MAP
CDM Field Supervisor:
Name of CDM Emergency Contact
CDM Local Office Phone:
Tim Williams
Chris Marlowe (phone numbers above)
(313) 291-3617
Signature of Health & Satefy Coordinator:
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F'FEB "13 . ;"'97"'05:3'lPM "'CDM fNJ)f~~~p(trSKEL
I"'.o!."~
P.2/2
FEB 13 '97 05:26PM
it,
BEALTBANDSAF"ETY PLAN
,FIEIJ) SAMPLING
SOLm WAStE'CBABACTll1n7.4.TIONANALY5IS
Camp .Dn&Ser'A McKee, IDe.
EMEllGENCY CONlAcr~ChrisMarlowe
(901) 22S..7OG at:m"
, (800)313-5593 (24J1our)
.
J
Rarltu 'Iaza OIle
IdSIoD, NJ 01118
(901) 225.7800
1. A copy' of d1is'Heald1 md Safety PJanmust be.kept OIl site daring the entile :sampling eyent. ,':
, 2.. All Pie1d Sampling .taff muSt complete two copies of the emerpncy QO!ltact foan, Ap.peDdJx A. to this
Plan. One copy of the emergencycontac;t foam for each ~raff person must be attached'to this PIaD and kept ,
on sill daring ,tbc cnliceaampliag.evei1t.The HCODd copy of the fomllDUltbe left with !be COM
emergency CQIltaCl: staff 81 theloc:a1 CDM office.
3. The following iDfoDDBtioa, for eachsampUDa sUe. znuat be ~p1ior to ~md"l the lampliDJ
event.
'. ~
J
Name gfJ.,lu)dfillor SaD)p1i1'l1 Site.:
Dates at Site: '
fiZ8 Phone Number:
Ambulanc:e PhoAe Number:
, . . P~Pbono Number.
Nc;areatHospital with EmeraencYFaciJity.
Name:' .
HospitalPhcme:
HOlipital AddD:8s: .
Ccmtact Name:.
DJrec:dGDS from site to lIospilal:
, SaUna MuDi.cipa1 SoJ1d. Wute Landfill
,11/11/96 to H/1Sl96a 2117197 to 212~7
911 or 826-7340 ,- ,)
'823..38& (TACBMS)
911 or 826..72.10
SaJinI Rcgicmal Hea1%h CeIltet
45~7000
400 S.Santa Po, SaliDa. ICJmIM
DUma KaDcIaon
North oa Bunua RDad tuCrlwfOl'd Street,
'GortcJlt (east) to luta 'e A.YlDUs
Go left (1lOIth) to BoIpItaI (011 the lell)
,1M ATTACHED MAl
.
CPMF1el4 superviaor:
Name ofCDMEmergenc1 Corltact
C1>M LocalOfficePhooe: .
Tim Williams
: C1uis Marlowe (Phouenumbln above)
(313) )91-3617 ..
C~~~
'SipatureotHca1th "S~CoordiDator.
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HEALTH AND SAFETY PLAN
TABLE OF CONTENTS
SECTION
PAGE
1.0 ' INTRODUCTION
1
2.0 OVERVIEW OF FIELD SAMPLING SAFETY
1
3.0 ELIMINATION OR REDUCTION OF POTENTIAL FOR BODY CONTACT
3.1 Clothing
3.2 Hand to Mouth Contact
3.3 Accidental Exposure to Waste
1
4.0 ANTICIPATION OF POTENTIAL THREATS
4.1 Weather Conditions
4.2 Crew Visibility
4.3 Crew Behavior
4.4 General Health of Crew Members
4.5 Rejecting a Sample
4.6 Evacuation
2
5.0 VISUAL OBSERVATION OF WASTE
3
6.0 STAFF TRAINING
6.1 Training Session
6.2 Responsible Individual/CDM Field Supervisor
4
7.0 EMERGENCY PROCEDURES
7.1 Responsible Party
7.2 Safety Equipment on Site
7.3 On-Site Treatment
7.4 Off-Site and Professional Medical Treatment
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ATTACHMENTS
ATTACHMENT A
ATTACHMENT B
ATTACHMENT C
Equipment for Solid Waste Characterization Sampling and Sorting
Emergency Contact Form
Map of Salina (Route to Hospital)
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HEALTH AND SAFETY PLAN
FIELD SAMPLING
SOLID WASTE CHARACTERIZATION ANALYSIS
1.0 INTRODUCTION
The health and safety of field workers in a primary concern of COM. This document. was developed to
present guideline for personal safety during solid waste characterization studies (also known as "waste
picks") at landfills. This document will be reviewed by COM staff responsible for the field sampling events
and the Field Supervisor. The guidelines in this document will be reviewed during the safety and training
session required of all field staff. This document is not intended for sites containing hazardous or toxic
wastes regulated under federal or state laws.
2.0 OVERVIEW OF FIELD SAMPLING SAFETY
Field worker safety includes using all reasonable precautions to:
. eliminate or reduce the potential for body contact from solid waste and airborne waste or "flying waste;
. anticipate potential threats to field worker safety;
. permit visual observation of the solid waste prior to handling or sorting;
. provide adequate information and training to enable field workers and COM supervisory staff to
perform the sampling in a safe and responsible manner; and,
. provide procedures for responding to emergencies.
3.0 ELIMINATION OR REDUCTION OF THE POTENTIAL FOR BODY CONTACT
Oue to the presence of bacteria, sharps, and other potentially dangerous materials in solid waste, the
following precautions and procedures will be followed by all field workers during all solid waste sampling
events. These are intended to minimiie field workers coming in contact with solid waste and airborne solids.
3.1 Clothing
Personal Clothing All field workers are to wear: ankle length pants; socks; sturdy boots or shoes with
reinforced toes, and long sleeved, loose fitting shirts. No sandals or canvas shoes will be worn during the
sampling.
Safety Clothing: COM will supply the following safety equipment: respirators or dust masks, hard hats,
safety glasses, safety vests, disposable or other coveralls, disposable latex gloves, and puncture resistant
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outer gloves such as Best's 65NFW or Ansell-Edmont's Orange Heavyweight. All field workers are required
to wear hard hats, safety glasses, safety vests, coveralls, and the puncture resistant gloves during sampling
and sorting. Disposable, latex inner gloves are not required but recommended to eliminate the hand from
which the first outer glove is removed .from touching the remaining dirty outer glove. Respirators or dust
masks are not required but will be present for use in the event that waste materials becomes airborne.
Hard hats may be coded by number and all field workers given a corresponding number. This is intended to
insure that the hats are used by only one individual throughout the sampling event. Hard hats and safety vests
will be brightly colored to increase visibility of workers in the sampling area.
3.2 Hand to Mouth Contact
No eating, smoking, drinking, or application of cosmetics will be permitted during the sampling. The crew
may perform these behaviors during breaks after washing their hands, and if required by the field supervisor,
their faces.
Fresh water for drinking and hand washing will be kept at the site at all times. Breaks will be taken regularly
as indicated by weather conditions. Gloves will be removed before pouring or drinking water.
3.3 Accidental Exposure to Waste
No crew will handle any solid waste without gloves. Accidental skin contact with waste will require cleansing
with soap and water. A wash-up station will be available at the site.
All crew will have a tetanus shot within five years of the sampling. If necessary, CDM will cover the cost of
the shot for all field workers prior to beginning the sampling.
All crew will have a HB-Ig immunization one week prior to the sort. CDM will arrange for and cover the cost
of this shot.
4.0 ANTICIPATION OF POTENTIAL THREATS
Working in an active landfill presents a variety of potential dangers. The following procedures are intended to
improve field worker safety.
4.1 Weather Conditions
Sampling will not be done in adv~rse weather conditions such as heavy rains, snowstorms, thunderstorms, or
winds strong enough to lift sorting barrels.
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Fresh water and cups for drinking will be available at all times. Chairs or some place to sit will be available at
the sorting site. If the sampling occurs during the warm months, an ice chest with cold, wet towels will be
available at the sorting site. Any field worker exhibiting signs of heat exhaustion will be immediately
required to take a break.
4.2 Crew Visibility
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The sorting site will be located in an area out of the immediate waste hauling vehicle and landfill equipment
routes. The CDM field supervisor and the landfill supervisor will jointly agree on the sorting site. All field
workers will wear brightly colored hard hats and safety vests.
4.3 Crew Behavior
No field workers may arrive at the site under the influence of drugs or alcohol.
All field workers will wear personal and safety clothing as described in 3.1 above.
No smoking will be permitted at any time on at the sorting site.
No throwing or tossing of waste at a person will be permitted during the sampling.
All field workers will complete the CDM Solid Waste Sampling and Safety Training.
4.4 General Health of Crew
All crew members should be in good physical health.
4.5 Rejecting a Sample
The field supervisor will be responsible for determining if a sample is potentially hazardous or dangerous.
The sample will be rejected if it: contains potentially infectious hospital or medical waste; is soaked in a
liquid other than water; contains unidentifiable contents; contains hazardous waste or materials posing a
safety hazard; or has an unusual odor not like other solid waste. If such a load is identified, it will be reported
to th landfill supervisor for removal from the sampling area.
4.6 Evacuation
The field supervisor will be responsible for determining if circumstances warrant evacuation for the site.
5.0 VISUAL OBSERVATION OF WASTE
To reduce the potential for cuts or puncture wounds, all waste will be spread out and viewed prior or handling
or sorting. The waste sample will be selected from the site via a front end loader or similar machine. It will
be deposited on a separate tarp. Waste will be spread apart using a shovel or pitch fork. Bags will be
carefully lifted to the sorting table and broken open with a shovel. A shovel will be used to put loose waste
from the sample onto the sampling table. It will be further spread out with hand tools such as gardening
trowels so that contents can be visually examined prior to handling.
No field staff will pick UP an, armload of waste. No field staff will grasp or "hug" an unopened bag of waste.
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6.0 STAFF TRAINING
Understanding the procedures necessary to promote safety and knowing how to respond to an emergency
beforeit happens, are essential to ensuring worker safety. All field staff will participate in a waste
characterization training prior to beginning the sampling. The training will be held as close as possible to the
actual sampling and may take place during the first part of the day the sampling and sorting begins. The
training session will require no more than one to one and one-half hours.
6.1 Training Session
The field worker training will include:
Introduction
purpose for waste characterization study
intended use
method of compensation (if using outside help)
dates of sorting and rain dates
supervisory responsibility at site
Sampling and Sort Procedures
procedures described in the accompanying sorting procedure document
Health and Safety Plan
specifics described in this plan
6.2 Responsible I~dividuall CDM Field Supervisor
Safety during the field work is the responsibility of the CDM Field Supervisor. The supervisor must have
previous solid waste sampling and sorting experience. The Supervisor will make project level decisions
regarding compliance with this Health and Safety Plan during field operations. The Supervisor may
temporarily suspend work if there appears to be a threat to health and safety. The Supervisor, or one crew
member, will have a current, Red Cross First Aide Training Certification. The individual with the First Aide
Certification will be considered the project Safety Coordinator.
The Field Supervisor will:
. Ensure that appropriate personal protective equipment is available and properly utilized by all field
staff during the sampfing activities;
. Ensure that field staff are familiar with the Health and Safety Plan and trained in the work practices
necessary for safe and efficient data collection;
. Ensure that field staff are aware of potential hazards associated with site operations, such as broken
glass, heavy equipment, etc.; and,
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Be responsible for correcting any work practices or conditions that may result in injury to personnel or
exposure to hazardous substances.
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7.0 EMERGENCY PROCEDURES
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Most landfills and waste collection facilities have safety plans and procedures for the site. Prior to beginning
the sampling event, the facility supervisor will be contacted to receive site specific safety procedures. CDM
staff will follow the existing procedure for handing an emergency on site. ill addition, the following CDM
emergency procedures will be followed.
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For the purpose of this plan, an emergency is a situation or condition which could require temporary
suspension of sampling or field work. This includes but is not limited to: adverse weather conditions, fires,
accidents or injuries to field staff, and discovery of waste samples that contain materials which are potentially
hazardous.
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ill the event of a site emergency, such as a fire or release of hazardous chemicals, the landfill's safety
coordinator or the field supervisor will instruct the crew to leave the area by the pre-planned evacuation route.
ill general, CDM personnel will not participate in efforts to control facility emergencies.
7.1 Responsible Party
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The Field Supervisor is responsible for deciding whether a situation or condition is an emergency. The
Supervisor is responsible for deciding whether the situation requires evacuation, on site medical attention,
adjustments in procedures, or off site medical attention.
7.2 Safety Equipment on Site
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A variety of safety equipment will be kept on site throughout the sampling. Table 7 - 1 lists the necessary
safety equipment.
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7.3 On Site Treatment
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Minor injuries such as cuts, scrapes, and the initial stages of heat exposure, will be treated on site by the
Safety Coordinator or Field Supervisor who is trained in First Aide.
7.4 Off-site and Professional Medical Treatment
Unless the injury definitely requires frrst-aid only, the Field Supervisor will seek professional medical
assistance. If such an injury occurs the following procedure will be followed.
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Immediate emergency frrst aid treatment will be given at the site.
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The injured party will be transported immediately to the nearest emergency facility as identified on the
front cover of this Plan.
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The supervisor or a member of the sort crew as designated by the Field Supervisor will call the
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emergency facility to inform them of the injury and that personnel are approaching for treatment.
.
The CDM staff emergency contact will be called and asked to contact the person, on the emergency
contact form (ATTACHMENT A), identified by the injured party, to be called in case of an emergency.
The CDM emergency contact is a designated individual or individuals at the local CDM office who is
available during the sampling event to receive and make emergency phone calls for the sorting crew.
.
If the supervisor must leave the site, all field staff will stop work until a responsible CDM substitute
can arrive to supervise the sampling.
.
If the injury was the result of a cut or puncture from a sharp or needle, the item will be retrieved and
placed in a zip-lock plastic bag for further examination or testing.
.
A report explaining the incident will be submitted to all interested parties including but not limited to:
CDM client officer, CDM health and safety group, CDM client contracting for the sampling, landfill
owner, and the injured party. Accident reports will be filled out where necessary.
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ATTACHMENT A
Equipment for Solid Waste Characterization Sampling and Sorting
Personal Safety Equipment:
Dust masks
Hard hats (brightly colored, numbered, so workers use same each day)
Safety glasses
Disposable coveralls
Disposable under-gloves (up to 5 pairs I day I worker, so workers will not touch bare hand to outer glove
after ftrst glove is removed)
Over-gloves, puncture resistant such as Best's 65NFW or Ansell-Edmont's Orange
Safety vests (or brightly colored over-shirts)
Site Safety Equipment:
Copy of Health and Safety Plan with cover sheet completed
Copy of Emergency Contact forms for each fteld worker
First Aid Kit containing at a minimum:
eye wash, compresses, antiseptic wipes and spray, band-aides, gauze, ftrst aid tape, aspirin;
Vehicle to permit immediate site evacuation
Clean water and cups for drinking
Clean water and soap for washing
Ice chest with ice and wet towels (for hot weather)
Chairs or place to sit
Zip-lock plastic bags
Paper towels, rags, and tissues
Light colored tarp for shade
Portable phone
Sorting Equipment:
Copy of sampling procedure
Copy of selected trucks or routes to sample
Sampling sheet, clip board, pencil, waterproof pens
Front end loader or bulldozer and driver
Heavy duty cloth tarp, approximately 25' x 50'
Sand bags to hold down tarp
Sorting table (4 sawhorses and 3 sheets W' plywood)
Plastic sheeting
Staple gun (wi staples)
Five gallon plastic buckets (20)
Shovels, pitch fork, rake, gardening hand tools
Push broom
Sorting barrels (40 residential waste polycarts)
Duct tape for labeling barrels
3' x 3' digital scale with 20-hour rechargeable battery
Camera and mm
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ATTACHMENT B
Emergency Contact Form
NOTE: Two copies of this form are to be completed by every field sampling worker. One copy is to be
kept at the site during the sampling event. One copy is to be left with the CDM emergency contact
person at the local CDM office.
Name:
Home Phone:
Blood Type:
Date of Last Tetanus Shot:
Date ofHB-Ig Shot:
Medications Currently Taking:
Allergies to Medication:
If an emergengy occurs during sampling, please contact
Name:
Phone:
Date Completed:
Signature:
PA!.( I I rl IST~( ElF! D 0 ~I ,-) ~ ., J ~~ ~ ~--~
:;; it 1:;;1 ~ ::1 I J ld :!i ~J v;.SH_ Sf O~' .J n~
A H ~ B N:! AVE ~~ \:1 ; UJ
~ ARIET~Ai SALINA REGIONAL ~ z ~ ~..!!!9N} ) ~ ~_L~~o" __ i
~ ;~: HEALTH CENTER ~ ~ 8 ~ g I~ i ~ ~~ q-Q <9~":.;~
u ~ S - Cl- GYPSUM iA:J]STAPlER AVE ~ 17; 0-9"OP-V
~I-g ... (400 S. SANTA FE AVE.) l': Jdol' ~ ~ .. AVE ?-- _ HILLCREST KNOLL'
.f" I -10.;; ~"\\. u .. 2;-. 0 OJ LA
; I- ~ " ISM .... STACK AVE:! ....... i
i VI G '" ~...u~~ ..t~1 gl" UOAK~OALE (j o:lll";j'!: ~""; "ILLVIEW RO
VI .J Sf I Ill::! t: ~ OR ~~.. :> () M
Q WHIJ~J!.~ U S-"O-U H .,.,1; ~ 0.. GLEN A
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~ ~ 15 0 IHOLliA! VI :;;1 \;;1 \;; ~ ~ r if J: INOIANR' CLA~:!1 GLI;t~" $ t?'t VI '" 0 ''Il'
o f ~ ~ '" ST I- & .. MO~RI;bN I- ::::>>!; "~~ \ii I- {(V' \.'w
:; It"f "',w a ~.. ARMORVRO VI ~ j J: STI ~ J: ~ CENfERSf ~ ~NGTO~OR ~"$..ffi::: ~ ~
I- '-' "., ,!:;:j~ 0 X I-WASHIN TO:; Ul (~<( \VE~TCH;STERo. 0 STRATFORD OR ? ~"'?o ~
ill :: :i" OR UJ U .. PRi"JCO{T ST :!I ~lO ~I -,:; ~[ ~ '" ...
~ LOUIS o~ A.:3 ::: >~r r~r - )00 :: ffi a ELM ~ :1 ~ 0-
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CllAWFOROST y'::i, cr Z HAVEN" g: CHJ.RLE ST _ l-~tlSk" _; BLVD ~:~o(j, z I>: ~ OUACiii
_. 0 T VE z 1 ,r ... fI) GU 0 r-- .. Z(/I <q.: <(l-, ~ '" _ ~:...
. Q 'I>~.J, ELGIN II A j 0 ;:. ~ uJ 1/ PRESCOTT RL c WILBRE 0:..'" uP'l j:: ASPE ~
it OR!!! ! C I- r ::: I~ ~ ff RO' ST. '" c:l
1 0) I ~'J"";;;'IL"/Nf.,S.JSTI 11;1' g,o 8'~.:;;MILLJOOOOR~;FA;TUHOR '~-,'%~H' ~I- ~
92 ~ 00: '00: C'o Q". o. """B, 'AL(.~o: STII:Z" .!!Q.U ~ Z:II UJ~ cr ~ ..
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\=, Qlt" "'" 0,,-, "'1: 1'", .FJ VENA G 0 Z ~ I- ~~ BONO:c 0 OJ :>,.. 0 :I: ... ..
."1< "~"'" '" 0 ~ J..P.":I C .. '" I"' J .HM S 0: MELLINGER OR 0 ~ 0 a "w
PLUM 13 ~ "-s, '" FRANKLIN Sf FRANKLIN:II ~ .J~ I- .\NDe~ Z McADAM R ~ 0: Wi ~J:
gfmDrR ~ ~ ~ OJ "'l~" l> o:~....~ z ~..lli VI W WILS N "'b! -r- ~IST ~ ~ r~ iMERO:R ~ ~'i-o
.... ~ UJ > > 0 < < (I) NO -J <( a:: <nr Sf 0( 0( I ~ it. O~
:: ~ ~ 15 ~ C ~ 1ft 1ft I> ~ ~ ~~r-~ ~ -~ WILSON ~ I LA'I:;; t; ~O M~O.RN~~N..~A ~ ;;! 4VL is MA::~N .gl.~~
~ ID PUEBLO ZPQNCA '!: .. '" OJ :> . I ST J: ~ ~~ I.".... ~ Z 0 ~ ,.
~ ?~O~I! ~ R ~UBLIC J: ~ ili (J ~....t\;; ~ AVE ~ . ,S ~ ~ ff: REPUBL,,3.$ ~ ~ ~ ~ F~~~RI OR ... ;:
4'''1'' A APAHOE ~... zrc;~~'io: B~LOIT T AVF, 1-1 .I BEL IT ~ AVE I 9RAO~~~W~R
~ \ ~ICHEYENNEAVE cc. ~'llUO~-.-..or'''Z~::,," ,-II -If" "UJT.II\ .. _,.._. _.._ ...._ I~ ,Q
~~AVBEA~!~:~:fo:~~E{ ..., ~ 'AT" '.'"'''' I ~II 'f.J"""'/twl~P~ 'i!~I\1':,,.,'.I! ~ l.....-.
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1# 1- ~~~ W ~ V ~f ( )>
1'1>00:; VAEA .4' -,.." \ '-I'll
~~ PAGE II ,.<r ~ ...
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SUMMERS
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A 1.'1.' ACHMEN1.' C
Map of Salina (Route to Hospital)
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::1 ~~~:~:p:o~:::rs
Other Plastic Containers
. '11 Polyethylene Film
Polystyrene Foam
Other Plastic
T:i
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:::'1 Grass Clippings
Leaves I Other Yard Waste
,
i Clean Wood
I Treated Lumber
Textiles, Rubber, & Leather
Disposable Diapers
II Fines
: Aluminum Cans
:~ AJuminum Scrap
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Ferrous Metal
'"1 Batteries
dl Other Glass
Clear Glass Containers
j Brown GlaSs Containers
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Other
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Bricks
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White Goods
TUTAL
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23.4 3.8 9.6
28.0 13.6 7.6
11.0 5.8 2.0
17.6 4.2 9.4
48.4 5.8 9.6
1.2 1.0
2.6 1.2
2.0 0.4
1.6 3.6
16.8 2.6
2.6 0.6
6.8 0.6
0.2
0.8
5.0
0.6
3.2
1.0
0.6
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8.6
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0.0
10.8
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0.8
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20.6
2.0
5.2
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219.4 34.2 0.0 51.0 14.2 128.8 14.4 95.2 10.4. 52.8 29.8 0.0
0.0 0.6 0.0 4.6 2.8 0.0
0.0 0.0 0.0 0.0 0.0 0.0
9.4 6.0 0.6 2.6 12.8 4.2
8.0 0.6 6.2 0.6 2.8 5.4
61.4 14.2 11.4 18.0 22.6 9.6
1.6 0.4 0.6 1.6 1.6 1.4
0.8 0.6 0.2 0.0 1.0 0.2
0.0 0.0 0.0 4.0 1.6 0.0
16.0 3.0 2.2 5.0 2.6 6.0
1.6 0.0 1.4 0.0 4.0 0.2
0.0 0.2 0.6 0.0 0.0 0.4
0.0 0.0 0.0 0.0 0.0 0.0
10.6 3.4 4.6 0.6 3.4 3.8
6.4 1.2 0.0 0.6 0.0 1.4
3.2 0.0 0.0 0.0 0.0 0.0
10.6 1.4 2.6 0.0 1.6 3.4
0.0 0.0 0.0 0.0 0.0 0.0
0.0
0.0
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0.0
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Fall Waste Sampling Event. Composition By Weight
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0.0
0.0
0.0
0.0
20.6
26.0
0.0
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0.0
0.0
0.0
0.8
0.0
0.0
0.0
0.2
0.6
0.8
16.6
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22.4
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11.0
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0.8
10.2
16.0
0.8
2.4
0.6
0.8
4.8
0.4
1.4
3.2
0.0
0.0
0.0
0.0
0.0
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4.2
27.6
0.8
1.4
6.2
1.0 13.4 8.8 22.6 10.4 22.4 35.6 17.4 7.6 26.4 41.0 8.0 450.0
0.0 0.0 0.0 0.0 12.0 0.0 0.0 0.0 10.4 0.0 .0.0 0.0 40.6
0.0 149.8 45.0 38.6 109.4 50.4 5.4 1.4 48.8 6.6 38.6 22.0 1,166.2
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2.2
14.0
33.4
12.8
0.4 r 0.4 0.4 0.4 0.4 1.0 0.4
0.6 0.6 0.4 1.0 0.0 1.0 1.0
7.4
19.6
17.8
19.6
1.4
8.6
11.6
192
0.6 ,. 0.4 0.2 0.2 0.4 1.0 0.2
1.6 1.2 2.6 0.4 1.6 4.6 2.0
3.2 "4.8 11.4 6.0 9.8 9.2 4.0
0.2 14.0 0.4 0.4 1.8 1.8 0.4
3.8 . 0.6 4.8 16.4 11.0 24.6 1.6
3.2
0.4
0.2
0.0
0.0
0.0
0.0
2.8
0.0
0.0
00
0.0
0.0
0.0 0.0
0.0 . '0.0
0.0
0.0
0.0
0.0
00
0.0
5.2
0.0
0.0
0.0
0.0
0.0
0.0
0.0
1.0
0.0
6.2
0.0
6.2
1.6
0.2
0.2
4.0
0.4
18.4
0.6
1.6
0.6
1.0
4.6
0.8
4.8
..:.
..:.
0.0
0.0
1.8
13.2 62.4 126.6
0.0 0.0 0.0
10.6 1.6 162.6
16.6 0.0 125.8
307.6
404.4
34.4
125.4
475.2
14.8
27.0
24.6
41.8
151.6
34.6
106.6
580.2 128.8 91.4 117.6 196.4 241.6. 139.8 191.2 152.2' 181.4 231.0 137.8 84.2 371.6 134.0 181.2 216.0 280.6 152.4 140.0 163.6 115.8 262.8 233.8 4.725.4 196.9
11.2
0.8
0.4
16.6
15.2
54.2
21.6
0.6
0.4
1.4
1.2
4.6
1.0
5.2
0.6
1.8
1.0
1.0
1.2
1.2
2_2
1.6
9.0
8.8
0.4
6.6
2.2
1.6
0.2 0.6 9.8 2.0 10.6 4.2 1.0 6.2 0.6 0.8 1.4 0.8 4.0 0.8 0.0
M M M M M M M M M M M M M M M
6.0 5.0 25.6 11.0 8.6 13.6 0.8 12.8 U 1.8 0.2 7.8 9.8 3.2 2.0
4.2 22.8 1.6 0.4 0.8 1.4 0.0 8.8 0.0 11.8 1.4 4.8 6.8 10.6 0.8
19.4 2.8 6.8 10.6 35.6 15.6 4.6 22.0 5.2 5.0 12.6 43.0 13.6 20.6 7.6
2.6 1.0 0.6 0.6 0.6 0.4 0.8 1.0 0.4 0.4 1.6 0.2 2.0 0.4 1.0
0.0 0.4 0.2 0.2 0.2 0.2 0.2 0.2 0.6 0.2 0.2 3.0 0.2 0.6 0.2
~ M M M M M M ~ M M M M M M M
2.6 2.6 4.2 2.0 4.0 3.4 0.4 12.0 0.6 2.4 5.0 3.0 10.0 2.2 1.2
0.0 2.4 0.0 0.0 0.2 0.0 1.0 0.0 0.0 1.0 0.2 0.6 1.2 0.0 0.4
M M M M ~ M ~ ~ M M M M ~ M M
M M M M M M M M M M M M M M M
0.8 1.8 0.0 0.4 0.8 2.2 0.0 0.4 0.6 4.6 0.6 5.6 6.0 1.6 3.6
0.6 0.0 0.0 0.4 3.8 0.6 0.2 0.6 0.0 1.0 0.0 1.2 0.0 0.0 0.0
0.0 0.0 0.0 0.0 0.2 0.0 1.0 0.0 0.0 1.2 0.0 0.0 0.6 0.0 0.0
3.4 0.2 12.0 7.2 10.6 1.2 3.4 3.2 14.6 19.4 12.8 10.0 1.0 0.4 6.4
0.0 0.0 0.0 0.0 1.4 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.6 0.0 0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.2
2.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
00
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
2.4
0.0
0.0
0.0
0.0
0.0
9.2
20.0
8.4
27.2
0.2
0.4
1.4
15.4
0.4
0.6
2.0
32.2
0.8 0.4
2.4 0.2
1.4
1.2 0.4
1.6
4.6
3.2 0.0
11.6 3.4
0.2
0.2
1.2 0.2
5.0 2.8
9.4
4.0
1.2
12.6 16.2 395.0
2.6 0.6 25.2
0.6
0.0
7.8
0.2 0.0 10.2
0.4 0.0 7.0
12.4 1.4 112.0
0.6 7.6 22.6
0.2
0.0 0.0 4.0
0.0 0.0 0.4
3.0 0.0 65.4
0.0
0.0
7.0
1.8
0.4
4.4
0.6
0.0
0.0
0.0
0.0
0.0
0.0
1.0 2.2 23.0
0.0 1.2 7.8
2.4 0.4 132.6
0.0 62.6 66.2
0.4
0.0
0.0
0.0
0.0
0.0
0.0 14.2
0.0 0.0
0.0 1.8
0.0 0.0
0.0 18.2
0.0: 0.0
Commercial Waste
12.8
16.9
1.4
-
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- - - -; - -: - - - -; - -; -; - -
- ..:. - - ..:. - ..:. ..:. ..:. - ..:. - - - - ..:. - :n ::; ~::
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0.2 0.2 4.8 2.2 0.0 16.2 6.6 3.6 0.0 44; 1.2 0.2 9.0 4.6 1.6 5.2 15.6 75.6 4.4 I
21.6 6.6 57.4 17.8 31.8 33.0 22.0 59.S 114.0 16.6: 31.0 46.2 27.0 26.0 14.0 75.0 12.4 612.2 36.0
0.0 1.4 2.0 0.2 0.0 22.6 5.6 ~. 6.0 0.0 0.2 1.6 2.2 1.4 1.6 68.2 4.0
21.8 1.0 06 !
0.0 3.2 0.4 4.0 0.0 1.2 0.2 9.6 0.0 2.6 i 0.6 0.0 0.4 3.0 1.4 0.6 0.6 27.8 1.6
;
4.6 12.4 17.6 23.4 2.4 38.0 25.0 20.4 37.2 19.2\ 40.2 0.6 11.6 17.6 29.4 20.8 12.6 333.0 19.6
0.0 0.2 1.0 1.8 0.0 1.6 0.4 4.4 0.8 0.6 : 0.6 0.2 0.4 0.4 0.6 0.4 0.4 13.8 0.8
0.2 0.0 1.6 0.6 0.0 1.0 0.6 0.8 00 1.6 2.2 0.0 1.0 0.6 1.6 3.4 0.0 15.2 0.9
;
0.0 0.0 0.0 0.6 0.0 0.4 1.0 1.6 0.0 .u, 0.2 0.0 0.2 3.6 0.6 6.6 0.0 16.6 1.0
0.2 0.6 4.6 0.2 0.0 19.8 2.0 12 2.0 6.4 1.4 0.0 0.0 1.0 1.8 0.4 00 41.6 2.4
13.4 8.6 7.4 22.8 12.0 16.8 i 16.6 6.0
40.8 20.6 7.2 9.8! 2.4 6.8 16.2 6.0 2.2 215.6 12.7
0.2 0.6 2.6 0.6 0.0 2.2 2.6 1.8 2.4 0.6; 1.6 2.2 0.8 0.4 3.2 4.0 0.2 26.0 1.5
5.4 1.6 1.0 3.0 3.2 0.4 0.8 0.4 S.6 7.6: 0.4 S.8 0.6 10.8 10.S 3.4 3.2 70.0 4.1
20.6 3.4 38.8 70.4 0.0 58.6 42.6 25.6 16.4 11.6 74.8 1.0 23.6 15.0 41.6 61.8 33.4 539.2 31.7
0.0 0.0 0.0 0.0 0.0 0.0 1.8 0.0 0.0 O.Oi 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.8 0.1
0.0 14.2 7.0 0.0 0.0 3.0 0.0 0.2 0.6 00, 3.8 1.0 0.0 0.0 28.0 0.0 0.2 58.0 3.4
0.6 0.6 0.6 17.4 51.6 0.0 5.2 9.2 11.8 2.4 4.6 13.0 2.0 1.0 2.0 0.0 9.0 131.0 7.7
0.0 0.0 0.0 0.0 0.0 0.0 0.0 00 0.0 0.0 0.0 12.6 0.0 0.0 0.0 0.0 0.0 12.6 0.7
0.2 0.4 3.0 32.0 0.0 1.6 1.4 4.6 38.6 20.6 0.6 15.6 2.6 17.6 5.6 0.0 9.0 153.4 9.0
0.0 2.4 0.0 16.2 0.0 0.0 0.4 1.2 0.0 1.6 0.8 0.0 0.8 0.0 4.6 3.8 0.0 31.8 1.9
17.6 6.2 2.6 66.6 6.4 14.0 7.0 25.2 13.0 15.2 9.4 5.6 4.8 6.0 10.6 9.8 1.6 221.6 13.0
0.4 0.2 1.4 2.6 0.0 1.2 0.4 2.4 0.6 0.6, 1.8 0.0 1.6 0.6 2.4 0.2 0.2 16.6 1.0
0.0 0.0 0.2 0.2 0.0 0.0 0.2 0.2 0.2 0.2 0.6 131.6 0.2 0.2 1.2 0.6 0.2 135.8 8.0
0.0 12.6 0.0 0.0 0.2 0.0 0.0 0.0 0.0 0.0 0.0 1.4 0.0 0.0 0.0 0.0 0.0 14.2 0.8
0.2 0.0 0.2 5.2 0.6 18.0 0.2 4.6 1.0 9.4 2.0 0.0 0.8 0.6 20.8 0.2 4.4 68.2 4.0
0.0 0.0 0.0 15.6 24.2 1.0 0.0 0.2 0.2 0.0 0.4 4.0 0.0 6.6 0.8 0.4 52.4 105.8 6.2
0.0 0.0 0.0 1.2 0.0 0.0 4.8 0.0 0.0 0.0 0.2 0.0 0.0 0.6 0.0 0.2 0.0 7.0 0.4
0.0 0.0 0.0 0.6 0.0 0.0 0.2 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.8 0.0
0.0 0.0 0.4 4.4 0.0 0.4 0.0 5.6 0.4 3.8 2.8 0.0 1.8 1.2 2.4 12 0.0 24.4 1.4
0.0 0.0 0.0 2.4 0.0 1.0 0.0 1.0 0.0 0.4 0.6 0.0 1.0 0.6 2.2 0.4 0.0 9.6 0.6
0.0 0.0 0.0 1.2 0.0 0.0 0.0 0.0 0.4 00 0.0 0.0 0.0 0.0 0.0 0.4 0.0 2.0 0.1
0.0 0.2 1.4 1.4 0.0 39.0 0.2 0.2 0.2 2.8 ., 0.2 3.4 0.2 6.6 0.6 1.0 0.4 57.8 3.4
I
0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 .1 0.0 7.6 0.0 0.6 0.0 0.0 0.0 8.2 0.5
0.0 0.0 0.6 0.0 0.0 0.0 1.2 00 14 0.0 0.0 0.0 1.6 0.0 0.0 5.6 0.0 10.4 0.6
0.0 0.0 0.0 0.0 0.0 0.0 00 0.0 0.0 0.0 :i 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
"
0.0 0.0 0.0 0.0 0.0 0.0 0.0 00 00 0.0 " 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
i,1 0.0
0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 00 ! 00 0.0 0.0 0.0 0.0 00 0.0 0.0
0.0 9.4 0.0 0.0 71.0 0.0 0.0 45.0 00 0.01 1.0 0.0 0.0 0.0 0.0 0.0 0.0 126.4 7.4
0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 00 0.0:\ 00 00 0.0 0.0 0.0 0.0 0.0 0.0 0.0
112.8 97.0 162.6 300.4 198.8 297.0 155.8 I 246.4 267.6 140.4!1 205.6 257.4 99.0 132.8 206.2 212.8 159.6 3,252.2 19].3
5.2
19.8
0.6
1.1
1.0
1.7
6.3
1.4
4.4
18.8
1.7
48.6
5.3
0.0
6.8
5.2
16.5
1.1
0.4
0.3
4.7
0.9
0.2
0.0
2.7
1.0
0.3
5.5
2.8
0.6
0.0
0.1
0.0
0.8
0.0
ResidfComm
~ -
~ .. ~t
~ ~~::
383.2 9.3
1.016.6 24.8
102.6 2-5
153.2 3.7
808.2 19.7
28.6 0.7
42.2 1.0
41.2 1.0
83.4 2.0
367.2 9.0
60.6 1.5
176.6 4.3
989.2 24.1
42.4 1.0
1~24.2 29.9
257.6 6.3
12.6 0.3
316.0 7.7
157.6 3.8
616.6 15.0
41.8 1.0
146.0 3.6
21.2 0.5
180.2 4.4
128.4 3.1
11.0 0.3
1.2 0.0
89.8 2.2
32.6 0.8
9.8 0.2
190.4 4.6
74.4 1.8
24.6 0.6
0.0 0.0
1.8 0.0
0.0 0.0
144.6 3.5
0.0 0.0
7,977.6 194.6
8121197
:1
:1
.c..:I';
.",
L..I'
~,.:.
1....:.
;~I
~I
:.'.;..' :~. :.
,,:,".
Newsprint
Corrugated & Kraft Pape'r
High-Grade Paper
Magazines
Other Paper
PET Bottles
Clear HDPE Containers
Colored HDPE Containers
Other Plastic Containers
--.
'~:.I'
. ::~
~
~~.
Polyethylene Film
Polystyrene Fo.un
Other Plastic
Food Waste
Gr'3SS Clippings
Leaves I Other Yard Waste
Clean Wood
';~1
;"1
Treated Lumber
Textiles. Rubber. & Leather
Disposable Diapen
Fines
-I,
-'
Aluminum Cans
Alwninum Scrap
Other Non.FerTOU5 Meta!
TIn-Steel & Bimetal Cans
Ferrous Metal
Batteries
)
:11
...;1.-
J
:"Ii
:~':),
'..""
Other Glass
Clear Glass ~ontainers
Brown Glass Cont3.iners
Green Glass Containers
Other
Roofing Materials
Metal
""'1)
'c'j
Concrete
Bricks
Blocks
1
:1
~ypsum Board & Plaster
White Goods
TOTAL
,
;11
"1
:~~J
,I
FAlLSORTXLS. 'l- COMP
I
...
;.J
Fall Waste Sampling Event- Percentage Composition By Weight
Residential Waste
- N ~. -T - N ~. -T '" - c. ~ -T '" - N ~. -T '" 1 ~ - N ~. ." =
'" -c '" -c -c -c -c -c ~ -c -c -c -c -c -c '" -c -c ~ -c '" -c -c _ 0
":' ":' '" ":' '" '" '" ~ ":' ~ ~ ~ ;; '" '" ~ ~ '" ~ '" ~ '" :-:I '=
- - N '" N ~ -T -T :! -T '" ,,; ~ 11: .~
- - - - .... - - - - - - - - - - - - .... - - ~g
..:. - ..:. ..:. - - ..:. ..:. ..:. ..:. ..:. ..:. ..:. ..:. - ..:. ..:. - - - - ..:. ..:. ..:. :;;
- - - - - - - - - - - - - - - -
4.0'" 3.0'" 10.5'" 1.4% 22.29, 5.6'" 9.0'i'c 4.09r. 9.3%'; 7.31< 6.31< 4.6% 1.0110 4,4110 5.5~ 10.81le 3.8'k 7.8110 1.69, 16.0110 6.79, 7.9% 7.6'70 1.80/, 6.8% ~.8o/c
4.8% 1O.61le 8.3% 7.3'70 10.5% 1.6% 10.0'i'c 2.19, 3.9%~. 10.6% 9.51le 23.7% 24.5o/c 7.0'i'c 4.6% 9.8'i'c 7.7'i'c 7.01le 7.60/0 13.7% 13.09, 7.3'i'c 10,40/0 11.8'i'c 9.5% 5A%
..
1.9... 4.5% 2-2% 0.01le 1.0110 0.1% 0.191- 0.0110 0.0110 , o.n 0,41le 0.19, 0.71le 0.191: 1.2~ 0.19c 0.21le 0.50/0 0.19, 2.9% 0.5'i'c 0.21le O.lt?t: 0.31le 0.7% 1.1%
3.0'i'c 3.3110 1030/0 0.0110 2.6110 4.8% 2.7lJc O.4"k 4.7% , 1.01le 3.2% 1.6% 1.0% 3.8% 8,49< 0.4% 0.6% 3.1110 0.3110 0.3% 6.2'i'c 1.2% 0.8'" 0.61le 2.7% 2.7%
8.3'i'c 4.51le 10.51le 9.2% 10.60/0 7.0110 13.9'i'c 6.1% 14.8,%. 9.7% 9,4% 9.3% 19.71< 9.0'i'c 12,49, 8,4... 5.3% 19.3110 14.21le 13.1% 9.81le 13.31le 12.3% 1.7110 10.5% 4.2%
0.21le 0.81le 0.11< 0.71le 0.6% 0.2% 0,4110 0.2\10 0.3%; 0.2110 0.2% 0.31le 0.51le 0.3'i'c 0.3% 0.31< 0.29'1: 0.2% 0.7'i'c 0.4ge 0.59, 0.3110 0.31le 0.2110' 0,4% 0.2%
0,41le 0.9% 0.9'jl, 0.7110 1.21le 0.29c 1.01le 0.5'i'c 0,4% . 0.3% 0.2% 0.7% 0.01le 0.31le 0.70/, 0.2'i'c 0.61le 0.6% 0.8'i'c 1.1% 1.51le 0.5110 0.9~, 0.1110 0.6% 0,4%
0.31le 0.31le 5.51le 0.0110 0.6% 0.2110 1.99c 0.9% 0,4% 0.29, 0.1% 0.1% 0.51le 0.39, 0.19c O.8~ 0.2% 0,4110 0.8'i'c OA% 0,4110 U'k 0.51le 0.20/1: 0.7% 1.1%
0.3% 7.8o/c 0.71< 0.5110 2.19c 1.0% 1.19, 0.59, 1.1110 '. 0.7110 1.1% 0.31le 1.91le 1.2% 1.5110 0.7'i'c 0.31le 0.8% 1.09, 0.71< 0.51le 1.4% 1.29'c 0.0% 1.0% 0.6%
2.91le 2.01le 3.5% 1.01le 3.0110 2.6'i'c 4.39',; I.79, 1.1110 ' 2.6% 4.91le 4,41le 11.6'i'c 2.51le 3.0110 2.51le 2.61le 3.11le 5.99, 3.3110 2.91le 4.01le 4,41le 1.5110 3.5% 2.0%
0,40/0 0.5'" 1.1% 0.7% 0.7110 0.69, 0.3'k 0.2110 0.1%; 7.71le 0.2110 0.3110 2.1% 0.51le 0.3'i'c 0.6'i'c 0.3% 0.1% 1,4% 0.61le 0.21< 0.2% 0.5\1: 0.11le 0.8% 1.5%
1.29, 0.5'i'c 0.71le 1.2... 1.0'i'c 0.7% 1.0% a.I"k 2.51le .. 0.3% 2.1 Ile 11.9% 13.1% 6.6'" 1.29c 2.91le 0.61le 2,4% 1.0'i'c 3,4'i'c 0.91le 0.20/c 1.9\1: I.2Ile 2.4% 3.4%
10.3% 7.81le 12.5% 1.0% 7.61le 6.31le 14.99, II.3Ile 13.5% 9.29c 11.91le II.3Ile 1.2% 3.6% 6.6'i'c 12.51le 4.8'" 8.0110 23,4% 12,41le 4.61le 22.8'" 15.6% 3.4% 9.9% 5.8%
O.OIle 7.5% 0.01le 0.01< 0.0% 0.0% 0.01le 0.0% 00% 0.0% 3.71le 0.0% O.OIle 0.0'" 0.0110 0.0% 5.61le 0.0(.7c 0.0% 0.0% 6,4% 0.01le 0.01le 0.01< 1.0"'-(1 2.3%
37.8110 26.61le 0.0% 43,41le 7.21le 53.31le 10.3% 49.8% 6.8%.- 19.1'" 12.99, O.OIle 0.0110 40.3% 33.6% 21.31le 50.6'" 18.01le 3.5% 1.01le 29.8% 5.71le 14.7\} 9,41le 21.0% 17.8%
0.0% 0.5110 0.0% Bile 1,4% 0.0% O.l(.k 0.3% 6,41le 1.1% 4.61le 3.0% 1.2(.k 1.7% 0.4% 0,41le 0.61le O.31le 2.6% 0.61le 0.0% 0.0% 5.01le 26.7'" 2.5% 5.5%
0.0% 0.0% O.W 0.0'" O.OIle 0.0% 0.0% 0.0% 0.01< .0.01< O.O'k 0.0,", Il.09, 0.0% 0.0'i'c 0.0% 0.0% 0.0% 11.09, 0.09< 0.0% 0.01le 0.01le 0.0'"' 0,0% 0.0%
1.6% 4.7% 0.7% 2.2110 6.5% I.7'k 4.30/, 2.6% 16.8'"; 6.1% 3.7% 9.9'"' 1.0% 3.4% 3.6\10 1.0% 0.1110 2.8% 6,4% 2.3'" 1.2% 1.6% 4.0'" 0.7'" 3.7% 3.6%
1.4... 0.5% 6.8% 0.59, 1,4% 2.2% 3.0'"' 11.9'"' 1.1% 0.2% 0.3% 1.0% 0.0% 2A9I 0.0% 6.5110 0.6% 1.7'" 4.5'k 7.6'k 0.5% 8.1% 6.3'l- 0.0'k 2.9% 3.3%
10.6% 11.0% 12.5% 15.3% 11.5% 4.0% 13.9'l- 1.5% 4.5% 5.8% 15,4% 11.3... 5.5% 5.9% 3.9'i'c 2.8'l- 5.8% 15.3'"' 8.9'i'c 14.7% 4.6'"' 3.51le 4.8% 6.9'k 8.3% .t6%
0.3% 0.31le 0.7% 1,4% 0.8'" 0.6% 1.9'"' 0.5% 0,4% 0.3% 0.31le 0.3% 1.0110 0.3% 0.39, 0.2% O.N 0.1% 1.3'i'c 0.3'i'c 0.6% 1.0% 1.00;;. 0.3'"' U.6% 0.4%
0.11le 0.5% 0.2% 0.0% 0.5% 0.1% 0.0% O.21le 0.1% 0.1% 0.11le 0.1% 0.2'i'c 0.1'" 0,4110 0.1'k 0.1'" 1.1% O.I'k 0.4% 0.11le 0.5% 0.11le 0.0% 0.2% 0.2%
0.0% 0.0% 0.0% 3,4'" 0.8% 0.0% 0.1% 0.0% 0.0% 0.09< 0.0% 0.0% 0.0% 0.2% O.OIle 0.0% 0.01le 0.01le 0.0% 0.0% 0.0% 0.0'i'c 0.21le '0.01le 0.2% 0.7%
2.8% 2.31le 2.4% 4.3% 1.3% 2.51le 1.9'" 1.4110 2.8'" 1.1% 1.71le 2.5% 0.5% 3.2% 0.4% 1.3% 2.31le 1.1% 6.61le 1.6% 0.7% 6.79< 4.7\1: 0.6% 2.4% 1.7%
0.3% 0.01le 1.5% 0.0% 2.0% 0.1% 0.01le 1.3... 0.0% 0.01le 0.11le 0.0% 1.29'c 0.01le 0.0'" 0.61le 0.1% 0.21< 0.81le 0.0% 0.2% 0.2110 0.2'>0 3.3% 0.5% 0.8%
0.0% 0.2% 0.7% 0.O\r 0.0% 0.2% 0,41le 0.0% 0.0%. 0.21le 0.1% 0.3% 0.2% 0.1'" 0.01le 0.0'" 0.01le 0.21le 0.11le 0.0% 0.0% 0.0% 0.0'>0 0.0% 0.1% 0.2%
0.01le 0.09< 0.0% 0.0% 0.0% 0.01le 0.01< 0.0% 0.0% 0.0% 0.0% 0.01le 0.01le 0.0% 0.0% 0.0% 0.01< 0.09, 0.31le 0.0% 0.0% 0.0% 0.0'>0 0.0% 0.0% 0.1%
1.8% 2.61le 5.O\!c 0.5% 1.7% 1.6% 0.61le 0.9% 0.0% 0.2110 0.3% 1.6% 0.0% 0.11le 0,41le 2.5% 0.31le 2.09, Bile 1.1% 2.21< 6.0% I.lIle 0.01le 1.5% 1.6%
I.lIle 0.9% 0.0% 0.5% 0.0% 0.61le 0,41le 0.01le 0.0% . 0.21le 1.6% 0049< 0.21le 0.21le 0.0% 0.61le 0.09, OAIle 0.01le 0.0% 0.0% 1.6% 004'1 0.9% 0,4% 0.5%
0.6<;< 0.01le 0.0% 0.0<;< 0.01le 0.01le 0.0<;< 0.0% 0.0% 0.01le 0.1'i'c 0.0<;< U'i'c 0.0% 0.01le 0.79'c 0.0'i'c 0.01le OAIle 0.0110 0.0% 0.31le 0.0<;< 0.5'" 0.1% 0-3%
I.81le I.lIle 2.81le 0.0% 0.8% 104% 2.4% 0.11le 7.9<;< .' 4.0% 4.61le 0.9% 4.01le 0.99, 10.91le 10.7'" 5.9% 3.6% 0.7<;< 0.31le 3.9% 3.8<;< 0.9~, 0.2110 3.1% 3.1%
0.0% 0.0'" 0.0% 0.0% 0.0% 0.01le 0.01le 0.0,", 0.0'"' 0.01le 0.6% 0.0<;< 0.01le 0.0% 0.09, 0.0'" 0.01le 0.01le 1.0... 0.01le 0.01le 0.5,", 0.0'" 26.81le 1.2% 5.5%
0.01le 0.2<;< 0.O\!c 0.0% 0.0110 0.0% 0.0% 0.01le 0.0% 0.0% 0.01le 0.0% 6.21le 0.0<;< 0.19, I.3Ile 0.11le 0.0110 0.0110 I.7Ile 2.01le 0.0% 0.2'" 0.01le 0.5% 1.3%
0.0% 0.0'" 0.0% 0.0% 0.0% 0.01< 0.09, 0.01le 0.01le 0.01le 0.01le 0.0110 0.0% 0.0'" 0.0% 0.01le 0.01le 0.0% 0.09, 0.09, 0.01le 0.01< 0.0% 0.01< 0.0% O.(}%
0.0<;< 0.0% 0.0% 0.0<;< 0.0<;< 0.0<;< 0.0110 0.01< 0.0110 0.0% 0.3<;< 0.0% 0.0110 0.3% 0.09< 0.0% 0.0'" 0.0% 0.0% 0.0% 0.0% 0.0% 0.01le 0.0% 0.0% 0.1%
0.0'" 0.01le 0.0% 0.0% 0.0<;< 0.0% 0.0110 0.0% 0.01< 0.01le 0.01< 0.0% 0.09< 0.0% 0.01< 0.01le 0.0% 0.09c 0.0110 0.0110 0.0% 0.01le 0.0% 0.0'" 0.0% 0.0%
1.61le 0.0110 0.0% 0.0'" 0.0% o.olle 0.01le I.5Ile 0.0% 0.0% 0.01le 0.01le 0.0110 1.79, 0.0110 0.0110 0.0110 0.00/, 0.0110 0.09, 0.0% 0.0% 0.0% 0.0% 0.2% 0.5%
6.09, O.O~ 0.0% 0.01le 0.0110 0.01le 0.09< 0.0110 0.01le 0.01le 0.0110 0.0% 0.0110 0.01le 0.0% 0.0110 0.01le 0.09, 0.0110 0.0% 0.0% 0.0'" 0.0% 0.09, 0.0% 0.0%
100.0110 100.0% IOO.OIle 100.0% 100.01le 100.0'" 100.0110 100.0% 100.09, 100.0% 100.0'" 100.01le lCXlO"7c 100.0110 100.09, 100.0% I O(lO'k 100.0% 100.0% 100.0110 100.09< 100.0% 100.0'" loo.09/: 100.0% 0.0%
'",,..
Commercial Waste
- - N ~ -T '" -c - "! ~ ,! - N ~. -T '" - c,
-c -c ~ ~ -c -c ~ -c '" -c -c ~ -c -c -c -c -c ~
'" '" '" '" ~ 5:. '" ":' 'I ~ ~ ~ ~ '" ":'
- N 0' N '"' Ll '" ~. ] -g ~
- - - - - - - - - -
..:. - ..:. - ..:. ..:. ..:. ..:. ..:. - - ..:. ..:. - ..:. ~~
- - - - - - - '"'
O.l'#. O.2~ 3.0% 0.7110 0.09, 5.5% 4.2'?c I.5Ile 0.0% 3.1%:1 0.61le 0.1'7r: 9.19r 3.5~~ O.89r 2.49'r 9.R% 2.6'70 3.1%
19.1110 6.8% 35.39, S.9<k 16.0110 ll.l'k 14.1% 24.3110 42.6% 11.8% 115.1 % 17.9% 27.3o/c- 19.6110 6.8110 35.2<fr 7.8'7r. 18.6% 1I.Il%
0.0% 1,4% 1.29C O.l'k 0.09,; 7.6% 14.0<;< 2.39'c OA'k 0.4% l.9'1/: O.09'c 0.29, 1.2'1c 1.1% 0.7'k 1.09, 2.0% 3.6%
I
0.0% 3.39c 0.2% 1.3% o.m7r; 004110 0.1% Bile 0.01le 1.91le j 0.31le 0.01le OA9'r 2.3(.k O.7'1c O.3'7c 0,49, 0.9% 1..2%
4.1'" 10.8"7c 7.8<;< 1.2'k ,J 13.J9C 14.3110
12.81le 12.8% 16.01le 8.31le 13.91le 13.;110 119.61le O.29'c 11.7\} 9.89, 7.9C-Jc 10.5% 5.10/0
0.09, 0.29'c 0.6% 0.6% O.09f 0.5110 0.31le 1.81le 0.3% 0,4%1 0.31le O.I'1c 0.4"" 0.39'c 0.30/, O.2'?c 0.3110 OA% 0.4%
0.2'" 0.0% 1.0% 0.2% 0.0% 0.3% 0,41le 0.31le 0.0% I.lIle 1.I1le 0.0% 1.09r a.59c 0.89, 1.6~"?: 0.0"" 0.5% 0.5%
0.0110 0.0% 0.0110 O.2~7r: O.ll'k 0.1% 0.6% 0.61le 0.01le 1.3~' I 0.11le 0.01le 0.29r 2.79'r O.J'1c 3.1'1c 0.0110 0.5% 1.0%
;1
O.29'c 0.6'" 1.8% 0.1110 O.()'?... 6.7% 1.3% 0.51le 0.71le 4.6% , O.7'1c 0.01le O.OSr,- 0.89'- 0.99, 0.29c 0.09, 1.2% 1.8%
36.21< 21:2'1c 8.2110 2.9"k 3.7'k 7.7110 4.6'.< 4.91le 6.3\1: 7.0'" 8.1 Ile 0.9% 6.9"7r: 4.S9'r 7.9110 2.89.-: lA'lc 7.9% 8.6%
0.21le 0.6% 1.61le O.2'1c n.m"?: 0.79, 1.7110 0.71le 0.99< 0,4% ' 0.8% 0.91le 0.89r- 0.31le 1.6'1c 1.99i: 0.1110 0.8% 0.6%
4.81< 1.61le 0.6'" 1.0% 1.6% 0.11< 0.59< 0.29< 3.2<1c 5A9, 0.21le 3.49'c 0.69'r. 8.1'" S.29c 1.6'1c 2.0'1c 2.4% 2.3%
18.3% 3.5% 23.9110 23,41le 0.01le 19.7'" 27.3'" 10,4% 6.1'k 8.3'" I 36,41le OA'1c 23.8% 11.3% 20.2% 19.01le 20.99, 16.6% 10.6%
0.0% 0.09< 0.0% 0.0% 0.0% 0.0'1< I.2Ile 0.01le 0.0% 0.01< 0.01t 0.0% O.O<1r: 0.0% 0.01le 0.01le 0.09, 0.1% 1l.3%
0.0% 14.6110 4.3% 0.0% O.O'k 1.0110 0.0% 0.10;;, 0.2% 0.0'" 1.81le 0.4% 0.0% 0.0... 13.6'" 0.01le 0.19, 2.1% 4.6%
0.5% 0.6* 0,4% 5.8% 26.0% 0.0% 3.31le 3.71le 4,4% 1.70;;, 2.29'r 5.10/, 2.09'r 0.8'i'c 1.01le 0.0110 5.6110 3.7% 6.1%
0.0% 0.01< 0.0110 O.09'r IU)'i'c 0.0% 0.0% 0.01le 0.0% 0.0% 0.0% 4.99r 0.0% 0.0% 0.01t O.09f. 0.00;;, 03% 1.2%
0.2% 0,40;;, 1.8% 10.7'7r. 0.0'1, 0.5110 0.9% 1.91le 14,4% 14.7% 0.3'i'c 6.1% 2.69r 13.3'k 2.7% 0.0% 5.60/, 4.5% 5.4%
0.0,", 2.5110 0.00;;, 5,4'if. O.O'k 0.0% 0.3% 0.5% 0.09< 1.1% 0.4,", 0.09'r. 0.8% 0.0% 2.29'r. 1.8% 0.0'i'c 0.9% 1,4%
15.6% 6.4% 1.6'k 22.2(;7r. 3.2'i'c 4.7% 4.5'1< 10.21le 4.9% 10.8% 4.6% 2.2% 4.8% 4j'k 5.1% 4.6% La'"' 6.5% 5,4%
0,4% 0.2'k 0.9% 0.9'.1 0.0% 0,4% 0.3'"' 1.0<;< 0.2% 0,4% 0.90;;, 0.0% 1.6% 0.5% 1.2',i: 0.1% 0.1% 0.5% 0.5%
0.00;;, 0.01< 0.1% O.I'k 0.0% 0.0% 0.1% 0.11le 0.1% 0.1<;< 0.3% 51.1% 0.29r. 0.21le 0.61le 0.3'" 0.1% 3.1% 12.4%
0.00;;, 13.00;;, 0.00;;, 0.09, 0.1'i'c 0.09< 0.01le 0.00;;, 0.0% 0.00;;, I 0.01le 0.5% 0.0% 0.0% 0.0% 0.0110 0.01le 0.8% 3.1%
0.21le 0.0% 0.1% 1.7... 0.3% 6.11le 0.11le 1.9% 004<;< 6.79<' I 1.0% 0.0% 0.8% Ojo;;, 10.11< 0.1% 2.81< 1.9% 2.9%
0.0% 0.0% 0.01le 5.2% 12.2% 0.31le 0.01le 0.1% 0.\% 0.0<;< 0.29, \.61le (l.0% 5.00;;, 0,41le 0.2'" 32.81le 3.4% 8.2%
0.01le 0.0% 0.0% 0,4... 0.01le 0.01le 3.11< 0.01le 0.0% 0.00;;, 0.1% 0.01le 0.0'" 0.5'1< 0.0% 0.1'" 0.0% 0.2% 0.7%
0.0% 0.0% 0.01le 0.29<: 0.0'1< 0.0'" 0.1% 0.00;;, 0.0% 0.00;;, 0.01le 0.0'" 0.0'" 0.0% 0.0% 0.0'" 0.0% 0.0% 0.1%
0.0% 0.0* 0.2% I.5Ile 0.0% 0.11le 0.00;;, 2.31le 0.1% 2.71le I 1.41le 0,0'" 1.8% 0.91le 1.2% 0.6'" 0.0% 0.8% 0.9%
0.01le 0.00;;, 0.0% 0.81le 0.01le 0.39< 0.09< 0.40;;, 0.0% 0.3<;< 0.3% 0.0'" 1.0... 0.51le I.lIle O.29t 0.01le 0.3'70 0,4%
0.00;;, 0.01le 0.0'1< 0,4% 0.09'r. 0.0110 0.0% 0.0<;< 0.11le 0.0<;<' 0.0% 0.01le 0.0'" 0.01le 0.0% 0.2% 0.0% 0.0% 0.1%
0.0<;< 0.21le 0.9110 0.5% 0.0'" 13.1% 0.11le 0.11le 0.11le 2.0% 0.11le 1.31le 0.2110 5.0% 0.31le 0.51le 0.3% 1.4% 3.2%
0.0% 0.01le 0.0% 0.0'" 0.0'" 0.0% 0.0% 0.01le 0.0% 0.0% 0.0% 3.01le 0.0'" 0.51le 0.0110 0.0% 0.0'" 0.2% 0.7%
0.0'" 0.0% 0.41le 0.0% 0.0110 0.0'" 0.89< 0.01le 0.51le 0.0% 0.0'" 0.01< 1.6% 0.01le 0.01le 2.6% 0.0'" 0.3% 1l.7%
0.00;;, 0.09< 0.0110 0.0% 0.09, 0.01le 0.0'" 0.0% 0.01le 0.01le . 0.0<;< 0.0'" 0.01le 0.01le 0.0% 0.0110 0.0% 0.1l% 1l.0%
0.01le 0.0% 0.0% 0.0110 0.0% O.09t 0.09< 0.01le 0.01le 0.0%11' 0.01le 0.0% 0.09"r. 0.0% 0.0110 0.09, 0.09, 0.0% 0.0%
0.0% 0.01le 0.0110 0.0% 0.0% 0.0% 0.01< 0.0'" 0.01le 0.0'" 0.0110 0.01le 0.0% 0.0'" 0.0110 0.01le 0.09, 0.0% 0.0%
0.01le 9.71le 0.01le 0.0% 35.7% 0.0% 0.0% 18.3% 0.01le 0.0% 0;5% 0.0% 0.0% 0.0% 0.09< 0.09, 0.09, 3.8% 9.6%
0.01le 0.09, 0.0'" 0.0% 0.0% 0.0% 0.0% 0.01le 0.0110 0.0% 0.09, 0.09, 0.0% 0.0110 0.00/, 0.00/, O.09c 0.0% 0.0%
100.0'" 100.0110 100.0% 100.0110 100.0% 100.01le 100.0110 100.0% 100.0% 100.0~! 100 aile 100.0110 100.0% 100.0110 100.00/, 100.0110 100.09, 100.0% 0.0%
Resid/Comm
~ l ,
~ "
:;; Vi
5.0% 4.6%
13.3% 9.3%
1.3% 2.5%
2.0% 2..3%
10.5% 4.5%
0,4% 0.3%
0.6% 0.4%
0.6% 1.0%
1.1% 1.3%
5.3% 6.1%
0.8% 1.2%
1.4% 3.0%
12.7% 8.7%
0.6% 1.8%
13.2% 16.7%
3.0% 5.7%
0.1% 0.8%
.to% 4.4%
2.0% 2.8%
1.6% 5.0%
0.6% 0.4%
1..% 8.0%
0.4% 2.1%
2-2% 2...3%
1.7% .5.4%
0.2% 0.5%
0.0% 0.1%
1.2% 1,4%
0.4% 004%
0.1% 0.2%
2.4% 3.2%
0.8% 4.2%
0.4% 1.1%
0.0% 0.0%
0.0% 0.1%
0.0% 0.0%
1.7% 63%
0.0% 0.0%
100.0% 0.0%
8/21197
,I
,I
n--I.
L
~I
~.."
f?1
-
Newsprint
Corrugated. & Kraft Paper
High-Grade Paper
Magazines
:"."...1
~/
Other Paper
PET Bottles
Clear HOPE Containers
Colored HOPE Containers
;~I
':'~.
Other Plastic Containers
Polyethylene Film
Polystyrene Foam
Other Plastic
i.f1I'.".'
f:";
.,..
Food Waste
Grass CUppings
Leaves I Other Yard Waste
i.'.'.I~.<l
{
Clean Wood
Treated Lumber
,:1
-
Textiles. Rubber, ~ Leather
Disposable Diapers
Fines
Aluminum Cans
-~I.
~~
Aluminum Scrap
Other Non-Ferrous Metal
TIn-Steel & Bimetal CaJtI
Ferrous Metal
"1'
....\..
"".
Batteries
Other Glass
Clear Glass Containers
~'11
'".
Brown Glass Containers
Green Glass Containers
Other
~,
Roofing Materials
Metal
Concrete
Bricks
(~I
Blocks
Gypsum Board & Plasfer
White Goods
..:1
TOTAL
:.'..
~
-I
I
FAllSORTXLS. STAT1ST1CS
Residential Waste
Monday - 11111196
c
~
L
~
] .~
V;o
~
"
:J _
~~j
3.3~
2.0~
1.5~
3.6~
2.1~
0.2~
0.2~
2.29'c
1.4<;\
2.5%
1.8<;\
0.4<;\
0.2~
1.4%
0.7<;\
0.6<;\
Tuesday - 11/12196
~
;
""@
a8
~
"
::3_
""" "
<= >
~8~
5.3~
3.0~
0.3~
1.3~
2.9~
O.I~
0.3~
0.5%
4.5%
3.3%
3.9%
004%
0.1%
0.3%
0.5%
0.7~
Wednesday - 11113/96
!
"'2 ~
:-:l "=
] :~-
~
"
. - ~ ~
~8]
4.7<;\
4.0<;\
2.4%
1.8<;\
4A~
10.0%
7.29t:
4.7%
15.0~
2A~
'8.3% - 6.1~
oj~' 0.2~
7.89<
2.1~
4.1%
8.1%
2.6%
5.89',
4.1%
004%
2.3~
'1.2% ,.. 0.9%
0.5%
0.3%
0.2%
004%
1104%
0.3~
4. 7~ . 304%
0.1%.' 0.1%
0.7%
0.2%
3.1%
10.5%
0.3%
0.7%
0.8%
1.8%
0.3%
0.39', 0.2%
1.5%
2.6%
3.9%
0.2%
0.4%
0.79',
0.6~ 004%
1.09', 0.7~
0.39< 0.2%
0.9% 0.6%
3.7% 2.7o/c
0.0% #NUM!
23.9% 17.5%
2.79', 2.0%
0.0% #NUM!
6.4<;\
n.I<;1(:
0.2%
1.0~
5.2%
2.2%
6.8%
704%
0.7~
16.5~
2.3%
0.1%' 0.1%
0.6% OA~ 0.8%
3.7% 2.8~ 3.3%
3.2%' 2A~ 0.5%
5.7% . 4.2% 1.8%
4.8%' 3.5% 10.3%
1.7% 1.2% 1.7%
17.9% 13.2% 22.6%
1.5%' 1.1 ~ 0.7%
1.1~
1.2% 1.0% 1.2%
0.7~ 0.6% 2.7%
3.99',
4.5%
5.3%
0.0'"'
4.8%
0.0'"' #NUM! 0.0,",
304'"'
2.6%
0.7%
0.3% 0.2~ OA~
7.1,",
0.8%
0.2'i1-
0.2%
2.0%
0.6'i1-
0.2%
004%
0.6~
0.8'i1-
8.8<;\
004,",
0.1%
0.0%
1.8%
0.3%
1.0%
4A'iI-
0.3'i1-
0.1%
'0.1%
1.1%
0.5~
0.9%
7.9%
1.9~
26.9%
1.1%
0.4% 0.3% 1.1 %
5.0% 4.1~ 10.7%
3.7% 3.1% 0.0%
19.3% 15.8% 25.5%
1.9% 1.6% I. 7'i1-
O.79i:
0.9%
0.1% 0.1% 0.0%
0.0% #NUM! 0.0%
0.7% 0.5% 1.8%
06~ 0.5~ 01%
0.5% 0.4% 0.2%
1.8% 104% 5.1 %
0.3%
2.8% 2.0% 0.7%
0.09', #NUM! 0.0%
0.2% 0.1% 0.0%
0.0% #NUM! 0.0%
0.7% 0.59', 0.0%
lOO.O~ 0.0% #NUM! lOO.O~ 0.0% #NUM! 100.0% '0.0%
0.0% #NUM' 0.0%
#NUM! 100.0% 0.0% #NUM! 100.0% 0.09', #NUM! 100.0% 0.0% #NUM!
0.0% #NUM!
0.0%
0.0% #NUM' 0.0'"
2.3%
2.3%
12.3%
0.7%
0.2%
0.9%
2.9%
0.5%
0.2%
0.0%
2.5%
0.6~
0.1%
104%
0.0%
0.0%
0.0%
0.0%
0.0%
1.7%
3.0%
2.1%
0.5%
0.2%
1.7%
0.9%
0.7%
0.3% 0.3% 0.1 %
0.0% #NUM! O.O~
1.9% 1.6% 1.0%
0.5% 004% 0.2~
0.3% 0.2% 0.0%
1.2~ 1.0% 2.59<
0.0% #NUM! 0.0'il-
0.1% 0.1% 0.0%
0.0<;\ #NUM! O.O~
0.0% #NUM! 0.0%
0.0<;\ #NUM! O.O~
004%
0.8% 0.7% 0.39',
0.0% #NUM! 0.0%
0.0%
0.2% O.I~ 0.2%
0.0% #NUM! 0.0%
0.7% 0.5% 0.5%
0.3% 0.2~ 0.5%
0.0% #NUM! 0.3%
3.1 % 2.3% 2.9%
O.O~ #NUM! 0.1~
0.0% #NUM! 1.2%
0.0% #NUM! 0.0%
O.O~ #NUM! 0.1%
0.0% #NUM! 0.0%
0.7~ 0.5% 0.3~
0.09< #NUM! 0.0%
1.89',
2.5%
0.7%
3.3%
0.2%
0.1%
0.1%
0.8%
004%
0.2~
Thursday - 11/14/96
j
::::
7.5%
9.1%
0.8%
2.7%
11.8%
004%
0.8~
OA~
2.5<;\
3.1%
8.0%
0.5%
0.3%
0.0%
2.0%
0.3%
0.1%
""2 ~
:':l '=
~ .~
tiio
4.8%
3.3%
1.0%
3.3%
4.5~
0.2%
004%
0.3~
004% 0.2~
1.2% 0.7%
004% 0.3%
1.1% 0.79',
6.6% 4.1%
2.9% 1.8%
17A~ 10.8%
0.9% 0.5%
0.0% #NUM!
2.1%
3.1%
5.2%
004%
004'"'
0.0%
2.1%
0.3%
0.1%
0.1%
1.3%
0.2~
0.3%
4.3%
004%
0.9% 0.5% 0.1%
0.0% #NUM! O.O~
0.0% #NUM! 0.0%
0.0% #NUM! 0.0%
0.0% #NUM! 0.0%
0.09', #NUM! 0.0%
~
"
:j -
~ ~ ~
3.0%
2.1%
0.6~
2.1%
2.8%
0.1%
0.3%
0.2%
1.3%
1.9%
3.2%
0.3%
0.2%
#NUM!
1.3%
0.2%
0.1%
0.1%
0.8%
0.2~
0.2~
2.7%
0.2%
Friday - 11/15/96
~
5.8%
9.8%
0.2%
0.9%
904%
0.3%
0.5%
0.6%
0.9%
3.3,",
0.2%
1.1%
13.9'i1-
0.0%
9.9%
10.6%
0.0,",
2.1%
4.8,",
5.1%
0.8%
0.2%
0.1%
4.0%
1.2%
0.0%
0.0%
2.4%
1.0%
0.3%
1.6%
9.1%
Fall \Vaste Sampling Event - Statistical Analysis of Percentage Composition
"5
~ '>
:-::I 'J
Via
3.59',
2.3%
0.10/(."
0.3%
5.9%
0.1'i1-
0049',
0.5%
0.8% 0.7~ 1.0%
1.6% 1.5~ 35%
0.2% 0.2% 0.8%
0.9% 0.8% 2.4%
9.8% 9.3% 9.9%
0.0% #NUM! 1.0%
4.5~ 4.3,", 21.0%
14.2~ 13.5~ 2.5%
D.O"} #NUM! 0.0%
1.7'"
4.30/.'
1.87f
0.47f
0.3%
0.\%
3.1%
1.8%
0.0% #NUM! 0.1%
0.0% #NUM! 0.0%
3.2~ 3.0% 15%
0.6~ 0.69', 0.4%
0.3~ 0.2% 0.2%
1.99', 1.8% 3.1 %
15.3<;\
0.1% 0.1% 0.5%
0.09', #NUM' 0.0%
0.09', #NUM! 0.0%
0.0% #NUM! 0.0%
0.0'il- #NUM! 0.2%
O.Oo/c #NUM! 0.0%
'0
"
:.:i _
~jj
3.3<;\
2.2%
0.1%
0.3%
5.6<;\
0.1%
0.4~
0.5%
1.77f
4.0%
1.7%
004110
0.3%
0.1%
3.0%
1.7%
14.5~
Event Average
~
~
::::
6.8%
9.5%
0.7%
2.7%
10.5%
0.4%
0.6%
0.7%
3.7%
2.9%
8.3%
0.6%
0.2%
0.2%
2.4%
05%
1.2%
"E 5
11
~
u
~"3
l.: ;:
tft. ::: ~
~8:S
4.8%
1.6%
5.4%
1.8%
1.1%
0.4%
2.7%
0.9%
4.2%
104%
0.2%
0.1%
0.4%
0.1%
1.1%
0.4%
0.6% 0.2%
2.0% 0.7%
15% 0.5%
3.4% 1.1%
5.8% 1.9%
2.3% 0.8%
17.8% 6.0%
5.5% 1.8%
0.0% #NUM!
3.6%
1.2%
3.3%
1.1%
4.6%
15%
0.4%
0.1%
0.2%
0.1%
0.7%
0.2%
1.7%
0.8%
0.6%
0.3%
0.2%
0.1%
0.1 %
0.0%
1.6%
0.5%
0.5%
0.2%
0.3%
0.1%
3.1 %
1.0%
5.5%
1.8%
1.3% 0.4%
0.0% #NUM!
0.1 % 0.0%
0.0% #NUM!
0.5% 0.2%
Commercial Waste
Monday - 11/11/96
J
L
~
~ .~
:/iQ
'0
"
:j -
~ ~ ~
0.2~ #D1V/O! #OlV/O! 2.3%
19.!% #D1V/O! #DIV/O!
0.0% #D1V/O! #DIV/O!
0.0% #D1V/O! #DIV/O!
4.1% #DIV/O! #DIV/O!
O.()% #DIV/O! #DIV/O!
0.2% #D1V/O! #DIV/O!
O.G% #D1V/O' #DIVIO! 0.2%
0.2% #D1V/O! #D1V/O! 1.99',
36.29', #D1V/O! #DIV/O! 8.19<
0.2~ #D1V/O' #D1V/O! 0.89',
4.8% #D1VIO! #DIVIO! 0.9~
18.3'>0 #D1V/O! #DIVIO! 16.3%
0.0% #DIV/O! #DIVIO! 0.2%
0.0% #DIV/O! #DIVIO! 3.3%
0.5~ #DIVIO! #DIV/O' 6.0%
OJI% #DIVIO! #DIV/O! 0.0%
0.2% #DIVIO! #DIVIO' 204%
0.0% #DIV/O! #DIV/O! 104%
15.6,", #DIVIO! #DIVIO! 7.1%
0.4% #D1VIO! #DIVIO! 004'"'
0.0% #DIV/O! #D1VIO! 0.1 %
0.0% #D1V/O! #D1VIO! 2.2%
0.2~ #D1V/O! #DIVIO! 104%
0.0% #D1V/O! #DIV/O! 3.0%
0.0% #D1V/O! #DIVIO! 0.6%
0.0% #D1V/O! #D1V/O' 0.1%
0.09< #D1V/O! #DlVIO! 0.3%
0.0% #DIV/O! #DIV/O! 0.2%
0.0% #D1V/O! #D1V/0! 0.1%
0.0% #D1V/O! #DIV/O! 2.5%
O.O~ #D1V/O! #D1V/O! 0.0%
0.0% #D1V/O! #D1V/O! 0.2~
O.O~ #D1V/O! #DIV/O! 0.0%
0.0% #DIVlO! #DIV/O! 0.0%
0.1)% #DIV/O' #D1V/O! 0.09',
0.0% #DIV/O! #DIVIO' 7.69',
0.0% #D1V/O! #DlVIO' 0.0%
100.0% #D1V/O! #DIV/O' lOO.O~ 0.0%
Tuesday. 11/12196
~
14.9~
-t.lo/c
0.99',
lO.2o/c
004%
0.39',
~-~ ::;
.,
a~
2.39',
10.8%
5.6%
1.3%
5.29r.
0.3%
O.49'c
0.29c
2.6~ 1.7%
6.8% 4.6%
0.79', 0.5%
0.6% OA'iI-
11.6% 7.8%
0.59', 0.3%
5.8'i1- 3.9\1-
10.0% 6.7'>-
O.09'r #NUM!
-l..l'k
2.2~
7.6%
004"
0.1%
5.3'>0
2Ao/c
5.0%
1.2~
0.1%
0.6%
0.3~
0.2~
5.2%
0.0% #NUM! 0.0%
0.3% 0.29', 0.2%
0.0% #NUM! 0.0%
O.O~ #NUM' 0.0%
0.09', #NUM! 0.0%
14.3S'c 9.6% 6.19c
0.0% #NUM! 0.0%
'0
"
:j -
""" "
~ ~ ~
1.5%
7.N
3.8~
0.9~
3.5~
0.2%
O.2~
O.29r
2.7'}
1.5%
5.1%
0.29'r.
0.0'>0
3.6%
1.6'>0
3.3'>0
0.8%
0.1'ilc
004%
0.2%
0.1%
3.5%
Wednesday - 11/13/96
j
::::
1.5%
26.20/.
1.091:
1.9%
12.09',
0.8%
0.5'ilc
0.6%
1.99',
6.0~
0.79',
2.9%
8.3\1-
0.0'ilc
0.1%
3.3'ilc
0'()'7(:
10.3,",
0.5%
R.6<>-
0.5%
0.1'"'
0.0'>0
3.0'>0
0.1%
O.O~
0.0%,
1.7%
0.2~
0.0%
0.7%
~
:: .~
ao
1.6'"
15.59',
l.l%
1.9%
3.29c
(J.8%
0.6%
0.6~
2.3%
l.l~
0.2%
2.6%
2.1~
0.0%
D.l 'k
lA'k
0.0<;\
7.3'i1-
0.6'"'
3.3'>0
004'>0
0.0%
0.0%
3.3'>0
0.0%
0.0% #NUM! 0.1%
O.O~ #NUM! 0.0%
1.4'>0 1.3~ 1.0'ilc
0.2% 0.2% 0.6%
0.1% 0.1% 0.0%
1.19', l.l~ 1.4'i1-
0.0% #NUM! 0.7%
0.3~ 03% 03%
0.0% #NUM' 0.0%
0.0% #NUMI 0.0%
0.0% #NUM' 0.0%
1O.5~ 1O.0~ 0.10/0
0.0% #NUM! O.O~
~
"
:j -
~~g
=-.0=
1.5%
14.7%
1.0%
1.9%
3.0%
0.8%
0.6~
0.6~
2.2%
1.0%
0.2%
2.5%
2.0%
#NUM!
0.1%
1.3%
#NUM!
7.0'"'
0.5%
3.1%
004'>0
0.0'>0
#NUM!
3.1%
0.0'>0
Thursday. 11/14/96
~
:j
::::
2.89,
17.3%
1.19,
0.79',
11.8%
0.3%
0.7%
0.7'lr.
0.5%
5.6~
0.99',
3.5%
18A'ilc
0.0'>0
3.2%
2.291:
1.09',
5.0%
0.7%
4.3%
0.8%
10.5'>0
0.1%
2.5%
1.4<J
]g
3.89',
7A9c
1.2%
0.99',
7.19'c
0.19c
0.4'k
1.2%
004\1- 0.3'>0 ':O.lo/c
3.091: 2.29t ::2;'191:
I
004% 0.3% ' 1,.0%
3.3% 204% .:1',8~
13.5% 9.9'>0 ;,.5.0%
0.0% #NUM! :0.0%
5.9'>0 4.3% III %
1.7'" 1.3'>0 1.8'"
2.19c 1.69r: '0.091:
5.1%
0.9%
1.2'>0
0.6%
22.7%
0.2'>0
4.3~
2.1~
0.2% 0.1 % 0.0%
0.0% #NUM! 0.0%
0.7% 0.5% 1l.3%
0.5% 0.3'>0 0.1 ~
0.0% #NUM! 1),1%
2.1 % 1.5% <)04%
1.3%
0.7~ 0.5% !.3%
0.09c #NUM! Q.09f:
O.O~ #NUM! 0.0%
0.0% #NUM' (J.O%
0.2% 0.2% i).O%
O.O~ #NUM' O.O~
'0
"
"
~~
,~
~~~'r==
2.8'"
5.5%
0.8%
0.70/0
5.2~
0.19c
0.3'>0
0.8%
3.7%
0.7'>0
0.9%
0.5%
16.7'>0
0.2'>0
3.1%
1.5%
0.9%
! Friday" 11115/96
:-6.\91':
..,1.5%
: ~).S9C
'0.3%
;R.8%
(}.2%
" ;}89C
1.6%
2.8%
(J.9%
1.8%
0.1%
0.2%
[1.0%
104%
[6.5% 23.1 % 26.8~
~ '>
aa
5.29c
19.4%
O.29C
0.1\<
1.3%
0.0%
1.19C
2.29C
0.1%
1.0%
1.271
0.3%
5.N
0.0%
0.1%
4.0%
0.0'il-
4.0%
1.3%
2.5~
0.0%
0.1%
0.0'>0
1.9%
~
"
~~]
=-.0 =
6.09'(
22.6'k
0.3\.
0.1%
1.5'>0
O.l~
1.3':l-
2.69c
O.2~ 1.2%
1.2CX 7.9%
104% 0.8%
0.3% 1.4%
6.7'>- 16.6%
#NUM! 0.1%
0.19'1': 2.1%
4.6% 3.7%
#NUM! 0.3%
4.6%
1.5~ 0.9%
3.0% 6.5%
0.0% 0.5%
0.1% 3.1%
#NUM! 0.8%
O.l~ 0.1% 0.2%
2.2% 1.9%
0.0'>0 #NUM! 0.0%
OA~ 0.5% 0.8%
0.1 % 0.2% 0.3%
O.O~
0.1 ~ 0.2% 0.0%
0.29C 0.2% 1.4%
0.0% #NUM! 0.2%
1.9% 2.2~ 0.3%
O.09i: #NUM! 0.0%
O.O~ #NUM! 0.0%
0.01l #NUM' 0.0%
O.O~ #NUM! 3.8%
0.0% #NUM! (J.O%
Event Average
~
2.6%
18.6%
2.0%
0.9%
10.5%
U.4%
11.5%
0.5%
4.5%
3.4%
l
al
~
"
.g~
t: ~
~8~
3.1%
1.2%
11.0%
~A%
3.6%
lA%
1.2%
0.5%
5.1%
2.0%
0.4%
0.2%
0.5%
0.2%
1.0%
0.4%
1.8%
0.7%
8.6%
3.4%
0.6%
0.2%
2.3%
0.9%
10.6%
4.2%
0.3%
0.1%
4.6%
1.9%
6.1%
2.4%
1.2%
0.5%
5.4%
2.1%
1....%
0.6%
5.4%
2.2%
0.5%
0.2%
12.4%
4.9%
3.1'rD
1.3%
2.9%
1.2%
8.2%
3.3%
0.7%
0.3%
0.1%
0.0%
0.9%
0.4%
0.4%
0.1%
0.1%
0.0%
3.2%
1.3%
0.7%
0.3%
0.7% 0.3%
0.0% #NUM!
0.0% #NUM!
0.0% #NUM!
9.6% 3.8%
#NUM! lOO.O~ 0.0% #NUM' 100.0% 0.0% #NUM! l00.0~ O.O~ #NUM' 100.0% 0.0% #NUMl
0.0% #NUM!
Reside n tiaJJ Comm ercial
E vent Average
"
- "
;; .g 1:;
~ "S! .~ ~ ~' ~
a~ ~ ,j ..:
5.0% 4.6% 1.2%
13.3% 9.3% 2.4%
1.3% 2.5% 0.6%
2.0% 2.3% 0.6%
10.5% ~.5% 1.2%
0...% U.3% 0.1%
0.6% 0.4% 0.1%
0.6% 1.0% 0.3%
1.1% 1.3% 0.3%
5.3% 6.1% 1.6%
0.8% 1.2% 0.3%
2.4% 3.0% 0.8%
12.7% 8.7% 2.2%
0.6% 1.8% 05%
13.2% 16.7% 4.3%
3.0% 5.7% 1.5'rD
0.1% 0.8% 0.2%
4.0% 4.4% 1.1%
2.0% 2.8% 0.7%
7.6% 5.0% 1.3%
0.6% 0.4% 0.1%
1.4% 8.0% 2.0~D
0.4% 2.1% 0.5%
2.2% 2.3% 0.6%
1.7% 5.4% 1.4%
0.2% 0.5% 0.1%
0.0% 0.10/(1 0.0%
1.2% 1.4% 0.4%
0.4% 0.4% 0.1%
0.1 % 0.2% 0.1%
2.4% 3..2% 0.8%
0.8% 4.2% 1.1%
0.4% 1.1~D 0.3%
0.0% 0.0% #NUM!
0.0% 0.1% 0.0%
0.0% 0.0% #NUM!
1.7% 6.3% 1.60/,
0.0% 0.0% #NUM!
100.0% 0.0% #NUM!
8/21/97
I
I
...,..",
>:1
I
..."..,
.1
I
Newsprint
Corrugated & Kraft Paper
~
I
'.'"
; :,~ ::
r
High-Grade Paper
Magazines
Other Paper
PET Bottles
Clear HDPE Containers
Colored HDPE Containers
Other Plastic Containers
'1
Polyethylene Film
Polystyrene Foam
Other Plastic
A
rl
Food Waste
Grass Clippings
Leaves I Other Yard Waste
Clean Wood
."""1
(.
I
:.,1
:;1
II
:1
"1
Treated Lumber
Textiles. Rubber, & Leather
Disposable Diapers
Fines
Aluminum Cans
Aluminum Scrap
Other Non-Ferrous Metal
TIn-Steel & Bimetal Cans
Ferrous Metal
Batteries
Other Glass
Clear Glass Containers
Brown Glass Containers
Green Glass Containers
Other
Roofing Materials
Metal
0']
Concrete
:"1
.-
Bricks
Blocks
;":.~i
Gypsum Board & Plaster
White Goods
_I
TOTAL
. ~
_I
"~t
I
WSORT.XlS . WEIGHT COMP
'1\
l
Winter \Vaste Sampling Event - Composition By \Veight
Residential Waste
- 0; .., -: - N ~, ;! ~ . -;f 0; .., "T ":' ;f r- - ~ '" r- N
r- r- r- r- .... r- .... r- r'- r- r- r- r- .... r- N ~, -: ;;
~ '" ~ ~ ~ ~ '" '" ":' '" ":' '" '" ":' ":' ":' ~ 3:: ,.:. r- r- r- r- r- r- ,.:. " -
r- x oC :: oC '" ;;, ;;, '" '" '" ~ '" ":' '" 3: ":' ~ ":' C - '"
- - - - - - - ~ ~ ~
N N N N N N N N N N N N N c, N N ~ ~j c, ~ ~ N ~ N = .~
c. e, N e' N 'J) ~J.::
18.2 20.8 16.4 18.6 10.2 22.2 11.4 5.2 8.0 36 12.6 12.6 27.2 4.0 11.6 6,4 8.8 3.8 10.8 8.8 9.2 5.6 4.0 10.6 7.8 \5.4 293.8 1I.J
18,4 30.4 15.6 22.6 20.0 14.2 19.6 14.8 6.0 18.2 29.0 30.2 23.2 28.2 35.8 8.6 13.2 20.2 22.0 18.0 15.2 11.0 22.6 16.2 29.6 17.6 520,4 20.0
17.4 2.2 3.8 2.2 0.4 6.6 1,4 0.2 0.6 .U 9.8 0.6 5.0 0.2 0.2 1.6 0.0 0.2 0.6 0,4 0.2 1.8 0.2 2.0 0.2 0.0 59.0 2.3
7.6 4.4 7.6 7.4 1.8 6.6 3.6 2.8 10.6 2.6 21.0 17.2 1.6 0.2 0.4 0.6 1,4 0.0 \.0 1.6 0.6 1.6 6.6 0.6 1.0 2.6 113.0 4,3
28.8 42,4 33.0 28.6 21.6 10.6 4.8 27,4 16.6 17.6 49.0 27.2 12.0 10.2 29.6 30.6 23.6 8,4 16,6 17.6 15.6 14.4 23.6 31.0 12.2 9.6 562.6 21.6
0.2 1.6 0.4 1.0 0.4 0.4 0.4 2.6 0.0 1.6 3.8 4.4 0.6 0,4 2.6 1.0 0.6 0.4 0.4 2.0 0.4 1,4 0.2 0.8 1.4 3.2 32.2 1.2
3.6 2.6 1.8 1.6 2.2 1.8 0.2 0.6 0.4 0.8 1.4 1.2 2.6 0.2 0.6 0.6 0.8 1.2 0.6 0.8 0.4 1.0 0.4 2.2 1.0 2.0 32.6 1.J
0.2 2.6 1.0 0.4 0.2 0.2 0.2 0.2 3.4 .1.2 3.6 1.0 0.6 0,4 0.4 0,4 0.4 0.2 1.6 1,4 0.4 0.2 0.2 0,4 0.2 2,0 23.0 0.9
2,4 2.2 0.6 0.6 2.0 0.4 0,4 2.0 0.6 .0.2 2.6 1.2 0,4 0.2 1.0 0.8 0.8 0.0 0.6 0.4 0.4 0.4 0.2 0.8 1.6 0.4 23.2 0,9
12.6 14.6 11.6 10.6 9.4 8.6 4.2 6.6 4.0 5.6 12.8 12.2 7.6 3.2 8.8 6,4 7.8 2.8 8.6 6.6 4.8 5.6 4.6 9.8 6.2 3.2 198.8 7.6
0.4 1.0 1,4 3.2 0.2 1.6 0.6 0.6 0.2 ,0.6 2.0 U 0.8 0.2 0.2 0.2 0.2 2,0 0.6 2.0 1.8 1,4 0.2 2.6 2.0 0.0 27.1 1.0
4.0 1.6 3.6 3.8 0,4 1.0 1.0 3.4 0.6 4.2 2,8 1.6 2.2 1.2 4.4 0.2 U 0.4 1.6 1.0 1.0 2.2 0.6 2.6 1'.0 2:6 50.1 1.9
3U 21.6 24.4 13.2 29.0 46.8 22.4 12.8 24.0 15.6 36.6 16.6 24.6 18.4 34.6 41.6 11.6 16.6 55.6 25.6 20.6 46.0 11.4 39.6 14.6 22.2 677.2 26.0
0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
1.0 0.0 0.4 0.0 22.2 0.6 0.2 0.0 1.0 ;0.0 0,0 112.4 7.2 6.6 1.8 0,4 0.0 0.8 0.0 0.0 0.0 0.0 2.0 0.4 0.0 1.0 158.0 6.1
0.0 0.2 8.8 0.4 0.2 0.4 3.2 1.6 0.4 8.2 0,6 0.6 0.0 0.0 0.8 0.0 1.2 0.0 0.8 1.2 5.0 0.4 2.8 0.6 0.0 0.0 37.4 1.4
0.0 0.0 0.0 1.8 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 U.U 0.0 0.0 U.O U.O 0.0 0.0 0.0 0.0 0.0 0.4 0.0 0.0 0.0 n 0.1
4.6 4.4 42.6. 16.4 2.2 1.2 0.4 32.6 15.6 3.6 8,6 1.8 2.8 .t.2 4.4 2.8 0.2 0,4 25.8 3.4 5.6 0.6 33.2 4.2 1.2 5.6 228A 8.8
30.0 7.4 13.0 11.4 3.0 2.6 2.4 2.2 15.6 8.6 5.6 8.6 13.U 2.6 6.4 16.8 3.6 0.6 7.6 O.U 14.6 17.6 1,4 4,4 1.8 1.2 202.0 7.8
8.6 15.0 17.2 20.0 10.6 14.6 3.0 9.6 6.6 4.6 24.4 17.0 5.6 6.6 9,4 2.2 5.6 8.8 11.6 9.4 7.6 19.6 2.0 3.6 4.0 5.8 253.0 9.7
0.4 2.2 1.6 0.6 1.4 0.2 0.4 0.8 0.4 2.0 3.4 2.6 1.0 0,4 1.4 0.8 n.2 0.6 1.4 1,4 U.2 0.8 0.2 1.6 2.4 \.6 )(l.0 I.l
0.2 0.4 1.6 0.4 0.2 2.6 0.0 1.0 0.2 0.6 1.6 0.2 0.4 0.1 0,4 0.6 0.0 0.2 0.2 0.6 0.2 0.0 0.1 1.0 0.8 0.2 14.0 0.5
0.0 3.6 0.8 0.0 0.0 0.0 0.0 2.6 2,6 2.0 0.2 0.0 O.U 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0 U 0.0 0.0 0.0 0.0 13.0 0.5
4.0 4,6 4.1 9.6 2.6 2.6 1.6 2.0 4.4 '0,8 10.4 7.4 5.8 0,4 5.2 3.0 3.0 4.4 5,6 8.4 2,6 4.0 0.8 6.4 3.2 2.6 109.6 4.2
0.0 3.4 0,6 8.4 0.0 13,2 0.0 0.0 1.6 0.6 28.2 0.2 0.0 0.2 2.4 0.0 0.2 0.2 0.0 0.0 0.2 0.2 1.0 0.0 0.0 0.0 no.6 2.J
0.2 1.0 0,4 0.0 0.0 0.0 0.0 0.4 0.2 0,0 0.0 0.2 0.2 0.2 0.0 0.0 0.0 0.0 0.0 0.2 0.2 0.2 0.2 0.0 0.2 0.2 4.0 0.1
0.2 0.0 0.0 0.4 0.4 U 0.0 0.0 0.6 0.8 0.4 0.0 0.0 1.0 0.6 0.0 0.2 0.0 0.0 0.0 0.2 0.0 0.0 0.0 0.2 0.0 6,1 0.2
3.0 5.4 0.0 1.6 8.8 2.2 0.0 U 3.2 ..3.0 11.0 8.8 6.6 2.8 2.2 2.6 4.2 0.0 6.2 7.0 1.6 8.2 1.6 9,8 1.0 2.6 104.6 4.0
0.0 0.2 0.0 0.0 3.4 U 0.0 2.6 2,6 ,0.4 0.6 U 0.8 0.2 0.8 1.6 0.0 3.0 2.4 7.4 0.0 1,4 0.2 1.0 0,0 0.0 31.0 1.2
0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.2 0.0 0.0 0.0 0.0 0.0 1.8 0.2 0.6 1.0 0.6 0.0 0.0 0.0 1.4 0.0 0.4 0.0 3.4 9.6 0,4
0.6 2.6 7.4 7.6 23.0 0,4 0.4 9.0 19.0 .13.8 23.8 23.4 6,6 1.0 U 10.8 0.6 1.8 3.6 3.8 11.6 6.6 0.0 0.2 3.6 0.0 182.4 7.0
0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 '0.0 0.0 0.0 0.0. 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0 0.0 0.0 '0,0
0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
0.0 0.0 0.0 0,0 0,0 0,0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0
00 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0
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b '" b b b b ~ ~ L. :.. '" Uo '" N L. iJ :., :.. b :.. 00 '" -... :.. 0- :., iJ b '"
" .. .. '" '" '" ", .. '" ", '" a'l '" '" ;jl '" " ;Il ,> " " " ;Il ;Il .. .. " ", ;Il .. '" " " " .. " " I>niatilln
8 '" 0::> 0::> 0::> 0::> 0::> 0 0 0::> 0 ~ 0::> '" 0::> 0- - -<0 C ~ C '-' '" 0 'J ~ - ~ 0::> 0::> ~ 0::> w 0::> 'J - -
-
0 0 0 0 0 0 0 -... 0 0 ;.;; 0::> 0 ~ ~ ~ ~ '" 0- C, 0 -... Co 0 C, ~ iJ ~ ~ 0 ~ ~ ~ ~ ~ ;.. 2.!7.YJ.1
Co " '" ?il " " " '" " " '" " " '" '" '" " '" " '" " '" " '" 1il '" :.,-0:
"
- '" 0 0 0 0::> 0 0 0 ~ '" '" 0 0 0::> 0 ~ .~ ,J '" '" - 0 - - 0 ". '" - ~ '" :--' 0 ", OJ 0
8 -<0 -<0
0 0 Co 0 0 0 0 ~ 0 ;;; ~ 0 0 ~ <=> 0 ~ ~ ~ ~ 0 iJ 0 <=> ~ ~ -... ~ ;J L, - ~ -... 00 ~ -... 2- \7-91-2
0 1il " " " '" " " " '" '" '" '" " '" '" c.::! " '" 1il ~ ~ '" '" " " ~
"
- '" 0 0 0 0 0 0 0 '" 0 0 '" 0 0::> 0 '" '" '" ~ <=; 'J 0::> 0::> 0::> OJ '" 0::> ~ - 0::> 00 0::> 'J - - 'J -
8 '0 a- w
0 0 0 0 0 0 0 ~ 0 0 0 0 0 0 io 0 io io ~ C ~ '" N 0 0 ~ ~ * iJ iJ 0 0 iJ ~ ~ o, 0 ~ 2-IIPn-1
0 " '" '" '" '" " " " '" '" " " " " " ",.:0. '" " " " " " ,> " " " " ~ 1il
;(l
:3 0::> 0::> 0::> 0::> 0::> 0::> 0 0 0 0::> 0 0 '" 00 ? 0::> '" - '" :--' 0 0 0::> '" ~ - 00 ~ 0::> '" .. 'J - ... ~
a- N '"
~ 0 0 ~ ~ 0 0 ~ 0 0 ~ 0 0 ~ - 0 0 - ~ c - 0 ~ 0 0 0 iJ '" 0 ~~ 0 0 ~ ~ 0 .. 2-1X-lJ7-2
0 1il '" '" " '" ;{l '" " " " '" " '" '" '" " " " 1il " " " " 1il " " "
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N
0 <=> 0 0 0 0 0 0 <=> 0 :;; 0 ~ <=> 0 ~ 0 <=> ~ 0 -... 0 ~ 0 iJ - ~ 0 ~ 0 - ~ .. 2-IX-lJ7-3
0 " '" " ;{l '" '" 1il " " " " " " " " '" " ~ 1il " ;{l ?il ?-,~ '" ?il " " " '" ""
?il
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~
0 ~ 0 0 0 0 0 0 0 0 0 0 0 ~ - - 0 ~ o, $ c, 0 ~ 0 0 ~ io iJ '" ;;; 0 * 0 o, <=> ~ 2-I!P)7-~
0 ?il 1il ?il '" '" " '" '" '" " '" ;(l " '" ;(l " " ,,-1 '" '" '" ,.,-Q ...::! " " " " " ?il 1il
1il
8 0 '" '" 0 0 0 0 'J '" 0 - 0 ~ 0 '" 0 0 'J ~ 0 '" '" - 0 0 a; - w - 0 0 - W 'J a- ;: ~
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0 " " 1il 1il ,1 '" '" '" '" '" 1il " '" '" '" " "... '" '" " 1il " '" " " '" :.{'.I " ",.0. ,,-0:
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0 0 0 0 0 0 0 c, 0 0 -... 0 0 -... iil 0 - - 0 ~ ~ 0 ~ 0 <=> ~ ~ -... ~ - ~~ ;.;; ~ ~ '" ~ 2.11).97.1
0 ,> " '" '" '" " 1il 1il " '" " '" '" " " '" '" ~ " " " '" \-'-1: ;.:,.::1 ~ :;l
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8 '" 00 '" 0 0::> '" 0::> .. ~ 0::> '" 0::> '" 0::> ~ '" '" ~ 0 '" 0 'J ~ 0::> <3 ~ ~ ~ 0::> 0::> ~ ~ .. 0::> 0::> !:; ~
0 0 0 0 0 0 0 ~ ;;; 0 ~ 0 0 0 ~ ;;; ~ ~ ~ 0 ~ 0 ~ - <=> ~ ~ ~ 0 - - L. 0 C, 0 u, 2_11).1)7_2
0 " '" " ;{l " '" '" " " " " '" " " " ~ '" <t"l " '" " " ~1 " ~1
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0 0 0 0 0 0 0 ~ 0 rz ~ 0 0 ~ ~ ~ ;.. ~ .~ ~ 0 ~ ~ $ .... ~ - .~ - ~ ~ - ~ ~ -... L, 2-I'P.J7-3
0 '" 1il 1il '" 1il ;{l " " '" ;(l " " " " '" " '" ~ '" "
- ';;,Q .~-- -- -- - -._"- - .-- -- -- .. . - '~.,._-..- " - -. d- .- .- '- -
- 0 '" 0 0::> 0::> '" 0 ~f 0 0::> '" 0::> 0 'J '" '" 0::> '" ~ 0 '" ~ 0::> 0::> "' "' 0 ~ 0 - 0::> 0 ", 0::> - 0 0
8 0 0 0 0 0 0 0 -... 0 0 0 0 0 ... ~ 0 0 iJ ~ 0 ~ 0 ~ 0 $ ~ 0 o, $ -... 0 iJ ~ '" 0 0 0 2-llJ-lJ7-..J
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8 0 0 0 0 0 0 0 iJ 0 0 0 0 ~ ~ 0 - 0 ~ 0 c, 0 <=> ~ ~ ~ v. ~ ~ L, ~ ~ .... ~ ~~ 2-20-97.1
0 " ;{l " " '" '" 1il :.,~ " '" '" '" '" '" '" '" '" " " " 1il " " '" ~ '"
1il
- 0 0 0 0 0 0 0 0 '" 0 00 0 0 ~ ~ ~ 0::> 0 '" 0 '" 0 'J 0::> 0::> 'J - '" -<0 0::> 00 0::> '" - 0::> 0 '0 '"
8 ~ - 0
0 0 0 0 0 0 0 0 0 ~ 0 0 0 ~ ;;; ~ 0 ~ 0 0 ~ 0 '" 0 0 -... '" 0 0 0 ~ 0 ~ Co 0 '" 0 2.~O.l)7-2
0 '" '" '" " " " " " '" '" " " '" " '" " " '" " '" '" '" '" '" ,1 " '" '" " :.{'.I
1il
0::> 0 0 0 0::> 0 '" 0::> '" :;: ~ 0::> 0 '" - 0::> 0 '" 0 '" '" '" '" '" 0::> 0 '" '" OJ <=; 0::> '" '" - 0 0 .. '"
8 ~ N
0 0 <=> 0 0 0 0 0 0 ~ 0 0 ~ ~ 0 .. -... 0 c ~ 0 0 Co C 0 - 0 c - - ~1 '=> - ~ - 2-10-lJ7-3
Co ?il 1il ",-0: '" " " '" " 1il '" " '" '" '" " '" '" '" " ....::J " ;-,-'-1: '" '" :.{'.I " ;..-"- :..,.::;, :.t' " .0 ",. :.0
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8 -
<=> 0 ~ ~ 0 0 0 0 0 ~ -... '" ;;; ~ - 0 $ a- ~ C, 0 c 0 <=> '" 0::> c. W - L, C, 0 -. '" 0 2-20-97--t
Co " " " '" '" '" '" '" '" " " '" " " " '" '" '" ,> :.,-1 '" ::.0: '" ~ ::.,Q ,0 ::,::l " '" '"
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15 Q Q Q C '" Q W Q C C Q 'J IJ ~ 1: '^ w '^ Q W 00 ... W Q '^ '" Uo 0- 0- '" 0- OJ '" '^
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r.
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I
f"
1 '1ewsprint
Corrugated & Kraft Paper
f-~igh.Grade Paper
I. \>Iagarines
0lher Paper
PET Bottles
~. .. .:::Iear HDPE Containers
I:o&oroo HOPE Containers
Other Plastic Containers
I~,~:t... olyethylene Film
. Polystyrene Foam
ther Plastic
Food Wasle
I~'::;rass Oippings
, '~Leaves I Other Yard Waste
CIC2l1 Wood
r Treated Lumber
Ir :fextiles., Rub~r. & Leather
:Disposable Diapers
Fines
-Aluminum Cans
"
1'.<\luminum Scrap
'Other Non-Ferrous Metal
Tin.Steel & Bimetal Cans
[-;~Ferrous Metal
!I:aatteri~
Other Glass
Iffi::lear Glass Containers
I'.'{~rown Glass Containers
Grttn Glass Containers
Other
8
I:::~~ Materiah
f: ,30cks
I'Blocks
;Gypsum Board & Plaster
White Goods
~
I
TOTAL
I
I
f('.,-1;
fic'.
I
SSORTXLS - \\.'EIGHf COMP
I
Spring Waste Sampling Event - Composition 8)' Weight
Residential Waste
N ~, ., - N ~, ., ~ ~ ~ - "! ~ ~ - '"
~ ~ r- r- ~ ~ ~ r- ~ r- ~ r- ~ r- r- r- r- '" ~, -; ... 'C j
'" '" '" '" '" '" '" '" '" '" '" '" '" '" '" '" '" '" '" ~ r- ~ ~ r- r- ~ " -
'" '" ~ '" ~, ~, ~, ~, ~, ~, ., ~ ., ., ., ., ., ... '" '" '" '" '" '" '" '" :=' ~
- - - - - - - - - ..., ..., ... .... 'C ~ - 0 = '!i
..., ~ ..., ..., ..., ~ ..., ..., .; ..., .;., ..., ..., ..., .... ..., ... .; .;., - - - - - - ~JS:::
..., ..., ..., ..., ..., .;., ..., .', :n
12.6 8.6 12.2 16,8 7.0 9,6 7.6 6.2 18.6 26.6 13.6 13.4 2.4 7.2 9,6 4,4 16,6 3.4 12,6 8.8 17,8 15.2 14,0 14.2 32,6 16,2 14.0 341.8 12.7
32.0 9,6 16,0 31.4 10,8 13.2 15.2 12.2 16,8 20,4 18,0 13,8 18.2 5,6 4.8 7,6 27,6 14,2 28,6 26.0 24.2 14,6 32,8 37.4 39,0 20.6 24,0 534,6 19.8
0.2 0.0 0,0 0,0 0.1 1.2 0,0 0.0 0,0 0.4 2,0 0,4 0,0 1.6 0.2 0.0 0.0 6.2 0.0 0.2 1.2 0.0 0.0 0.0 0.2 0.0 0,0 13.9 0.5
7.0 3,0 0,4 3,4 5.8 7.2 0.4 2,8 0,0 3.4 13.6 3.8 1.6 8,0 0.2 0.2 19,6 4.6 6,6 17.2 10.0 4,8 6.2 0,4 11.6 7,6 0.2 149.6 5.5
26,4 7,6 28,8 24,0 22,8 12,0 16.4 15,4 24,0 26,0 27,7 25.2 10,8 28,2 12,0 16.4 21.0 86.8 24.8 29.2 23.4 29,8 15,6 19,4 50.0 20,4 28,0 672.1 24.9
1.2 1.2 0,6 0,6 0.6 0.2 0.8 1,4 1.4 1.0 1.2 0,6 0,4 0.4 1.0 0,6 1.8 1.4 1.0 1.4 1.6 1,4 1.2 1,4 1,4 1.6 2.6 30.0 l.l
1.6 1.6 2.4 2.0 1.8 0.2 0,4 1.0 1.4 0,8 2.6 2.6 0.8 3.6 1.0 1.6 1.4 0.4 2.6 1.6 1.4 1.6 1.0 2.4 1,4 1.2 1,4 41.8 1.5
1.2 1.0 . 1.6 1.8 3.6 2.6 0.2 1.0 2,4 2.0 1.6 7,4 1.0 1.0 0,4 0,4 0,6 0,0 2.4 1.6 4,4 1.6 3.0 2.6 2.6 3,0 1.6 52.6 1.9
0.8 0,6 1.0 1.8 2.0 0.2 0.2 0,6' 2,4 0,2 0,8 0,6 0,6 1.2 1.0 0.2 06 1.4 2.6 2.6 7.2 1.6 3.2 0.6 1.6 2.4 2.6 40.6 1.5
13,6 6,6 11.4 7.8 8,6 3.0 4.2 6,0 7.6 8.6 8.0 11.0 17.8 7.4 5,6 3.6 9,4 7.4 10,6 9,6 7.2 9,2 5.2 10,4 8.8 7,4 13,0 229.0 8.5
1.8 1.2 2.6 1,4 1.4 0,6 0,8 1.6 1.6 0.4 1.0 0.8 0.6 0,8 0.2 0.2 1.2 0,8 1.2 0,8 1,4 2,6 1.0 0.6 1.6 0,8 3.4 32.4 1.2
5,0 7,4 3,8 12,6 4,0 3.2 2,6 0,6 0,8 1.2 1.6 52 0.4 2.6 2,6 2.6 3,0 0,8 13,6 2.8 4.2 1,4 3.8 13,0 3.6 9,4 9,8 121.6 4.5
,28,8 16,6 8,6 26.4 28,6 5.6 3.0 17.8 21.8 12.8 30,6 12.2 7,8 8.6 6,6 26,0 15.6 5.2 30,8 26.6 32,8 19,6 22.0 5.0 15,4 23.0 32,6 490.4 18.2
12,6 0,0 110,4 0.0 2,0 2.4 0.0 6.2 9,2 5,8 8.0 0.0 0,0 0,0 37.6 0,0 0,0 0,0 28,6 \4.2 0.0 7,6 60,6 3.8 0,0 0,0 0,0 309.0 11.4
29,0 18,4 11.6 51.4 4.4 19,6 19,8 27.2 46.4 81.6 142,6 72,0 35,2 0,0 24,2 14,2 31.2 61.6 19,4 61.6 65.2 28,0 64.8 34,0 23.6 47,6 35,6 1,070.2 39.6
0.4 4,0 3,6 9,4 0.2 0.0 1.2 3.2 5,0 0.2 3,0 02 3,6 3.0 3,0 2,2 9,0 0,0 2,8 13,0 5,8 0.4 3.2 6,0 2.0 0,0 6.2 90.6 3.4
0,0 0,0 16.0 10,4 0,0 0.2 0.0 0.0 3,8 0.0 13,8 0,4 4.6 0,0 0,0 0,0 0,0 2.0 0,0 0.0 0,0 0,0 1.8 1.8 0.0 0,0 1.6 56.4 :.1
10,6 3,6 6,8 16.8 6.6 31.6 2.6 12.4 2.6 3,0 6,4 3.4 1.6 5,0 5,2 1.2 39,4 2.2 27,8 16,4 10,0 5,6 3,0 23,6 2.2 22.6 42,6 314.8 11.7
14.0 5,6 1.0 20.4 0,4 2,6 1.2 0,0 1.2 7,0 9.6 18,2 4,6 2,0 13,6 13.2 0,0 0,2 9,6 2.2 5.2 13,0 2.0 3.6 15,8 0,0 4,0 170.2 6.3
17,4 10,2 17,4 11.2 9.2 n 0,8 17,6 7.0 11.6 17,0 8,0 3.6 29,0 5,6 9.6 4,8 7,8 7,6 3,6 4,6 2.6 12.6 20,M 7,6 6.2 15,0 278.2 10.3
0.8 1.2 1.4 4,0 2.2 1.6 0.4 0,4 1.4 1,4 2,6 1.4 0,1 1,4 0.2 0,8 1.6 1.8 4.2 2,4 2.0 1.6 1.8 4,6 1.6 1.6 5,8 50.3 1.9
0.6 0,0 1.0 0.2 0,2 0.0 0,4 0.2 0,6 0,2 0,2 0.2 0.3 0,0 0,1 0.2 0,1 0,0 1.4 0,1 0,1 0,4 0.2 0.2 0.2 0.4 3.2 10.7 0.4
0,4 0.0 0,0 0,0 1.2 0,4 0,2 0,0 0,2 0.0 3,6 1.6 0,0 0,0 0,0 0.2 0,0 0,0 1.2 1.2 0,0 0.0 0,0 8.0 4,4 0,0 0.0 22.6 0.8
4,6 1.6 7.2 4.2 4,4 0,4 1.4 3,2 6.2 1.4 3,6 3,6 2.6 1.0 1.0 0,8 7.4 1.2 9.6 3,6 5,6 4,8 3.2 4,8 6.2 4,6 7,4 105.6 3.9
1.0 0,0 9,6 0.0 0.0 3,6 0.0 0,0 1.4 0,6 4.0 0,4 1.8 13,4 0,0 1,4 0,0 1.8 5.2 0,4 0.2 0,8 1.8 6.6 0.2 6,0 16.0 76.2 l.&
0,0 0,0 0,0 0,0 0,0 0.2 0,0 0,0 0.0 0,4 0,5 0.1 0,0 0.2 0.8 0,0 0.2 1.0 1.2 0.2 0,0 0.0 0.2 0,0 0.0 0,0 0.6 5.6 0.2
0,0 0.0 0,0 1,4 3.0 0,0 0,0 0.6 0,0 0,0 0,2 0,4 0,0 0.6 0,0 0,0 0,0 0,0 0,8 0,0 0.0 0.2 0,6 0.2 0,4 0.4 0,6 9.4 0.3
1.6 0,0 1.8 5,6 3.2 0,4 0,6 6,6 2.0 0.4 0.2 4,6 2.0 2,0 3,8 3,4 2.4 0,1 7,6 2.2 3,8 9.8 8.0 2.8 9,6 5,0 2,6 92.1 3.4
0,4 0,0 0,0 2,6 1.2 0,0 4.0 1.6 1.0 0.0 1.6 ' 0,8 0.4 0,0 0.2 0.2 0,0 0.6 0,0 0.2 0,6 0.0 4,6 0.6 4,2 0,0 1.0 25.8 1.0
0,0 0.0 O,O~ 1.2 1.2 0,0 0.0 0,0 0,0 0,0 0,2 0.6 0.0 0,6 0.0 0,0 0.2 0,0 0,1 0,0 1.0 0.0 3,6 0.2 2.2 1.4 3.4 15.9 0.6
3,8 0,0 0,8 2.8 1.0 4,6 0.6 0,4 3,6 3,0 3,0 7,6 1.8 2.0 1,4 0,0 3,6 1.8 3.0 0,6 7.2 2.0 2;6 17,2 3,0 9.6 10,6 97.6 3.6
0,0 0,0 0,0 0,0 0.0 0,0 0,0 0,0 0,0 0,0 0.0 0.0 0,0 0,0 0,0 0,0 0.0 0.0 0.0 0,0 0,0 0.0 0,0 0,0 0,0 0,0 0,0 0.0 0.0
0,0 0,0 0,0 0,0 0.0 0,0 0,0 0.0 0,0 0.0 0,0 0.0 0.0 0,0 0,0 0,0 0.0 0.0 0.0 0.0 0,0 0,0 0.0 0,0 0.0 0,0 0.0 0.0 0.0
41.6 0,0 0,0 0,0 0.0 0.0 0.0 0.0 10,0 0.0 0,0 0.0 0,0 0.0 0.0 0,0 4.0 0.0 0.0 7,8 0,0 0,0 0.0 0.0 0.0 0,0 0,0 63.4 2.3
0.0 0,0 0.0 0,0 0.0 0,0 0.0 0.0 0,0 0,0 0,0 0.0 0,0 0.0 0,0 0,0 0.0 2.0 0.0 0,0 0.0 0,0 0.0 0,0 0.0 0,0 0.0 2.0 0.1
0,0 0,0 0,0 0,0 0,0 0,0 0,0 0.0 0.0 0,0 0,0 0.0 0,0 0,0 0,0 0.0 0,0 0,0 0.0 0,0 0.0 0.0 0.0 0,0 0,0 0.0 0.0 0.0 0.0
0,0 0.0 0,0 0,0 0.0 0,0 0,0 0,0 0.0 0.0 0,0 0.0 0.0 0,0 0.2 2.4 0.0 0,0 0,0 0,0 2.4 0,0 0.0 6.8 0,0 0.0 0,0 11.8 0.4
0,0 0,0 0,0 0.0 0.0 0.0 0.0 0,0 0,0 0,0 0,0 0,0 0,0 0.0 0,0 0,0 0.0 0.0 0,0 0.0 0,0 0,0 0,0 0.0 0,0 0,0 0,0 0.0 0.0
271.0 109,6 278,0 271.6 137,5 136.2 85,0 146,2 200,4 220.4 342.4 220.5 124,6 136.4 142,1 113.6 222.3 216,7 267,5 258,1 250.5 180,2 283.6 253.0 253.0 219,0 289,4 5.628.8 208.5
Commercial Waste
- '" ~, ., '" ~, ., ... '" ~, -; ~, - '" ~. ., .... -
~ r- ~ ~ ~ r- ~ ~ r- r- r- r- '" ~ r- r- r- r- r- r- " -
'" '" '" '" '" '" '" '" '" '" '" '" '" '" '" '" '" '" '" =-~
'" '" '" ~. ~, ~, ~, ~. ., ., ::': ., ., ~ ... ..., .;., ... 'C ~
- - - - - - - - - - - - - ;; = 'ij
..., ..., .;., ...., .,; .,; ..., ..., ..., .;., ..., ~ ... ..., ..., .... .... .;., :or. :; , ,.
..., :n_
1.8 11.6 0,2 4.6 7.6 2.0 1.4 0.0 0.0 5,4 19,4 2.0 0,6 1.8 2.2 0,0 1.0 5.0 0.2 21.8 4,4 93,0 4.4
5,0 33.2 27.6 11.6 13,8 19.6 24,6 41.4 27,0 .25,6 86.0 17,0 3.2 16,4 18.0 43,4 42,0 39.6 36,2 26.4 53,2 615.8 29.3
0,0 0,0 3.6 0,6 0.2 6.2 2.2 0.0 4.2 0,0 ~5.2 0,4 1.2 0.0 0,0 0,6 0,0 0,0 1.0 0.0 4.2 49.6 2.4
0.0 1.4 1.6 0.2 2.6 0.6 0.2 0,0 5.2 0.2 73.0 0,4 0,8 6.2 0,0 1.6 0,0 4,0 0,4 1.8 2.0 102.2 4.9
8.0 85.8 15.6 30,2 47,6 28.2 14,6 23.8 10.4 21.4 2.0 21A 9,6 8,8 10.4 50,0 8.6 8,6 5.0 35,4 54.8 500.2 23.8
1.0 2.4 0,0 1.2 0,4 1.0 0.6 1.0 0.0 1.2 1.2 0.2' i 1.6 0,8 0.2 1.0 2,4 2.2 0,8 0,4 2.6 22.2 l.l
0,4 0,6 0,0 0.2 1.0 1.2 . 0.8 1.6 0,4 0,0 0,6 O,g 0.6 0.2 1.2 0.6 1.0 1.6 0,0 0,4 2.8 16.0 0.8
0,0 0.8 0.0 1.6 0.0 4.0 0,0 G.I 0.4 \,4 0,6 0.4 1,4 2.2 5,6 0.6 0.6 2.2 0.6 9,6 3.8 35.9 1.7
'.
0,0 0.0 0,0 0,2 0,4 1.2 0.2 0,0 0,0 0.2 11.6 0,6 .' 1.0 0,5 1.0 0.4 0.0 0,6 0,6 0,4 2,6 21.5 1.0
4.6 6.6 22,0 16.2 6.6 10.6 5.2 0,6 6.6 6,8 0.8 2,8 I 5.2 11.8 11.8 8,0 13,4 10,8 18.6 9,8 11,4 190.2 9.1
1.2 0.4 0,6 6:6 2.2 1.0 1.2 1,4 0.6 3,4 16.2 0.0 0,4 1.0 1.2 1.6 0,6 1.8 1.2 2.0 5.2 49.8 2.4
7,6 0.8 2.6 3,6 1.0 1.0 4.6 44,8 0,4 2.6 6.2 0.2 2,8 2,4 12,6 7.6 6,6 16,g 6,2 2.4 2.4 135.2 6.4
6,2 19.2 0,0 225,6 3.6 5,4 52.4 72,0 19,8 19,6 0,0 12.4 3,6 14.0 34,4 3.0 16.2 30,6 0,0 60,4 80.6 679.0 32.3
0.0 0.0 0,0 0,0 0,0 32.2 31.2 0,0 0,0 0,0 0,0 0.0 0,0 0,0 0,0 0,0 0,0 0,0 0,0 0,0 0,0 63.4 3.0
0,0 10.6 0,0 1.0 0,0 0,0 2.8 16,2 0.0 0,0 1.0 25,6 0,0 0,0 0.0 0.0 26,6 0,0 60,4 0,0 3,8 148.0 7.0
7,8 0,0 4.6 21.0 0,2 5,4 0,0 10.2 0,4 3,4 3,6 2.8 21.6 6,6 0,2 31.8 0,0 7,8 19,8 0.2 0,9 148.3 7.1
0,0 0.0 0.0 0,0 0.2 0,6 0,0 0.0 0,0 0.4 1.2 0,0 0,0 0,5 0.0 4,6 0,0 0,0 2,0 14,2 0,0 23.7 1.1
19,8 0,0 1.6 0.4 6,8 0,0 0,4 7.6 0,2 4,8 5.6 5,0 4,6 26.2 0,6 12,8 17.2 18,6 11.6 10,0 0,1 153.9 7.3
0,0 2.6 0,0 2.2 3.0 0.0 18,0 0,0 0,0 0.6 0,4 5,6 2,2 0,6 0,0 1.6 0,0 10,8 0,0 G,O 1.6 49.2 2.3
44,6 1.0 1,4 14.6 2.6 2.2 16,2 2.6 1.8 8,6 13,4 7.2 10,6 5.6 0,4 12,0 24,8 6,2 45,4 0.2 4.2 225.6 10.7
3,6 8.4 1.0 1.0 1.2 0,6 0.6 1.0 0,8 0.1 2,6 0,4 0,6 0.1 1.2 1.4 0.8 2.2 1.4 1.0 1.0 31.0 1.5
1.2 0,4 0,0 1.0 0,0 0,0 0.2 0.0 0.2 0,4 0.4 0,0 0.0 0,6 0,1 2,0 0,4 0.0 0,1 0.1 0,1 7.2 0.3
15.2 0.0 0,8 0,0 0,6 0,0 0,0 1.0 0.0 0.0 0.0 0,0 41.6 0,0 0,1 0.0 2.8 0,0 0,0 0.8 0.0 62.9 3.0
0,6 O,g 0,6 1.0 0,6 3,6 4,2 0.2 0,2 2.6 10.6 2.6 0,6 8,8 0.1 8.6 4,6 1.0 7.2 17,4 3.2 79.1 3.8
16,8 0,0 0.0 5,8 0,0 1.2 0,0 0.8 0,2 0,4 0,8 1.5 0,0 1.0 5.2 5,0 1.6 3,6 1.0 0,4 4.2 49.5 2.4
0.0 0,0 0.0 0.0 0.0 0.0 0,0 0,0 0,0 0,0 0,0 0.0 0,0 0,0 0,0 0,0 0,1 10.0 0,0 0.2 0.2 10.5 0.5
0,0 0.0 0,0 0,0 0.0 0,0 0.6 0,0 0,0 0,0 35,4 0,8 1.0 0,0 0,0 2,8 0,0 0.0 0.1 0,1 1,4 42.2 2.0
0,2 0,8 0.0 9.2 1.2 0,0 1.2 0.2 0.8 3,6 2.4 1.0 3,6 0.4' 2.2 4,8 6.4 0.2 0,4 2,4 4,6 45.6 2.2
0,0 0,0 0,8 9,4 0,0 0,0 9,8 3.2 0,0 0,4 0.2 0,0 0,8 0.0 0,2 0,0 52,8 0.2 0,0 0,2 0,2 78.2 3.7
0.0 0.0 0,0 0,0 0,0 0,0 0,0 0,0 0,0 0.0 0.0 0,0 . 0,0 0.0 0.0 0.0 3.2 0,0 0,0 4.6 0.0 7.8 004
1.0 0.4 0,6 5.2 0,6 0.6 19,2 0,0 12.0 0,0 1.6 8,8 35,0 7.4 0.0 3,0 0,0 15,4 51.0 1.8 0.0 163.6 7.8
0,0 2.2 0,0 0,0 0,0 0,0 0.0 0,0 0,0 109,6 0.0 0.0 0.0 0,0 0,0 0,0 0,0 0,0 0.0 0,0 0,0 II J.8 . 5.3
0.0 0.0 0,0 0,0 0,0 0,0 0,0 0.0 0.0 0,0 0,0 0.0 : 0.0 0.0 0,0 0.0 0,0 0,0 0,0 0.0 0,0 0.0 0.0
0.0 0.0 0.0 0,0 0,0 0,0 0.0 0,0 0,0 0,0 0,0 0,0, . 0.0 0.0 0,0 70.0 0,0 0,0 0.0 0,0 0.0 70.0 3.3
0,0 0,0 0.0 0,0 0,0 0,0 0,0 0.0 0,0 0,0 0.0 0.0 0.0 0,0 0,0 0,0 2,0 0,0 0,0 0,0 0,0 2.0 0.1
0,0 \ 0,0 0,0 0.0 0.0
0,0 0,0 0,0 0,0 0,0 0,0 0,0 0,0 0,0 0,0 0,0 I 0,0 0.0 0.0 0.0 0.0 0,0 0,0
0,0 0,0 0,0 4,8 0,0 0,0 0,0 0,0 0,0 0.0 2.4 0,0 0,0 0,0 0.0 0.0 1.2 2.0 0.0 0,0 0,0 lOA 0.5
0,0 0,0 0,0 0,0 0.0 0,0 0.0 0.0 0.0 0.0 0,0 0,0 0,0 0,0 0:0 0.0 0,0 0.0 0,0 0,0 0,0 0.0 0.0
146,6 190,0 85,2 379.0 104,0 128.4 212.4 229.7 91.6 222,7 324.4 119,9 159,2 123,9 108,9 278,8 236,9 201.8 271.2 224.4 255.5 4.094.5 195.0
ResidlComm
" -
, }~
,;; ~~::
434.8 9.1
1.150.4 24.0
63.5 1.3
251.8 5.2
1.172.3 24,4 .
52.2 l.l
57.8 1.2
88.5 1.8
62.1 1.3
419.2 8.7
82.2 1.7
256.8 5.4
1,169.4 24.4
372.4 7.8
1,218.2 25.4
238.9 5.0
80.1 1.7
468.7 9.8
219.4 4.6
503.8 10.5
81.3 1.7
17.9 0.4
85.5 1.8
184.7 3.8
125.7 2.6
16.1 0.3
51.6 1.1
137.7 2.9
104.0 2.2
23.7 0.5
261.2 5.4
111.8 2.3
0.0 0.0
133.4 2.8
4.0 0.1
0.0 0.0
22.2 0;5
0.0 0.0 .
9,723.3 202.6
8121/97
I'.
I.
1
I
N~wsprint
Corrugakd & Kraft Paper
Higb-Grade Paper
i
Magazines
Othu Paper
PET Bottles
Clear HDPE Containers
I
1,"-.......
. ~::
Colo~ HDPE Containers
Other Plastic Containers
PolydhyJene Film
PolY5lyrene Foam
Other Plastic
Food Wask
Gnm Qipplngs
Luns I Other Yard Waste
~
1
Clean Wood.
Treated Lumber
Textiles., Rubber, & Leather
i
Disposable Diapers
Fl..,
Aluminum Cans
.1:
Aluminum Scnp
Other Non~FerroU5 Metal
TIn-St.cel & 8b~elal Cans
rtrrous Metal
Bauerles
ff
I:
fill;
I',
Other Glass
Clear Glass Containers
Brown Glass.Containers
Greea Glass Containers
Othc,
Roofing-Materials
M...I
I,""......
I' "; ~
Concrete
I
Bricks
Blocks
Gypsum Board & Planer
f;
I!
While Goods
TOTAL
ftm'
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I)
f
I
(:"1;
I;
SSORT.XLS.... COMP
I'
/'
Spring Waste Sampling Event ~ Percenlage ComJX)sition B)" Weight
Residential Wasle
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S; ~ ~ ~ ~ ~ ~ N '? '" c
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
N N N ~ :c :c .; ~ ..; .; ::: ~ '" c
- ~ .c c _
~. ~, ~. .,; ~ .r. ~, ~, .r. ~, ~. ~ ~ .;, .r. - - ~ ;
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11.8'k 8.8'k 5.8'k 11.6'k 7.9'k 9.7'k 17.9'k 8.n 8.4'} 9.3'k 5.n 6.3~ 14.6'K- 4.1'K 3.4'k 6.n 12.4'1- 6.6'1- 10.7'J- IO.I~ 9,n 8.1'k 11.6'k 14.8<1- 15.4'k 9.4'k 8.J'} 9.3'k 3.5"k
0.1'k O.W O.W O.W 0.1% 0.9'k 0.0'k 0.0'k O.W 0.2'k 0.6'k O.n O.W 1.2'k 0.1'k O.W 0.0'k 2.9'k 0,0'k 0.1'k 0.5'k 0.0'k O.W 0.0'k 0.1'k O.W D.OIK 0.39, 0.69"
2.6'} 2.7'k 0.1'k 1.3'k 4.n 5.3'k 0.5'k 1.9e;. O.W 1.5'k 4.W 1.7'k 1.3'... 5.9'k 0.1'k 0.2CJ. 8.8e;. 2.1'1- 2.5'k 6.n 4.O'k 2.n 2.2'K 0.2'1- 4.6'k 3,5'k 0.1'k 2.6'k 2.3%
9.7'k 6,9'k ID.4"k 8.8'k 16.6'k 8.8'k 19.n 10.5'k I2.W 11.8'k 8.1'k 11.4'J- 8.n 20.7'1: 8.4'k 14.4"k 9.4'k 4Q.I'k 9.n 11.3'k 9.3'k 16.5'k 5.5'k 7.7'k 19.8'k 9,3% 9.n 12.39, 7.0"ic
0.4'k 1.1"k o.n o.n 0.4'k 0.1'k 0.9'k l.W 0.7'k 0.5'k O.4'k 0.3% 0.3'k O.J'k o.n 0.5'k O.N 0.6'k 0.4'k 0.5'k 0.6'k 0.8'k 0.4'k 0.6'k 0.6'k 0,7'k 0.9'k 0.59", 0.3%
0.6'k 1.5'} o.n 0.7'k 1.3'k 0.1'k 0.5'k O.n o.n 0.4'k 0.8'k 1.2'k 0.6'k 2.6'k o.n 1.4r;. 0.6'k o.n I.W 0.6'k 0.6'k 0.9'} 0.4'... 0.9'k 0.6'k 0.5'k 0.5'k 0.89", 050/,
0.4'k 0.9'k 0.6'k 0.7'k 2.6'k 1.9'l- 0.2'k D.7'k 1.2'k 0.9'k 0.5'k 3.4'k 0,8'k 0.7'k O.J'k OA'k 0.3'k O.W 0.9'k 0.6'k 1.8'k 0.9"1- 1.l<1- I.W I.W 1.4% 0.6'k 0.99', 0.8'7,
0.3'k 0.5'k 0.4'k 0.7'k 1.5'k 0.1'k 0.2'k 0.4'k 1.2'K 0.1'k 0.2'k o,n 0.5'k O.n 0.7'k O.2'k 0.3'k 0.6'k I.W I.W 2.9'k o.n 1.I'k o.n 0.6'k 1.I'k 0.9'k 0.7"7, 0.6%
5.W 6.0'k 4.1'1- 2.9'k 6.3'k 2.2% 4.9'k 4.1"k 3.8'k 3.9'k 2.J'k 5.0'k 14.3'1- 5.4'k 3,n 3.n 4.n 3.4'k 4.0'k 3.n 2.9'k 5.1'k 1.8'k 4.1'k 3.5'k 3.4'k 4.5'k .,U% 2.4%
o.n l.l'k 0.9'k 0.5'k I.W O.4'K 0.9'k 1.I'k 0.8'k o.n 0.3'k 0.4'k 0.5'k 0.6'k 0.1'k O.2'K 0.5'k 0.4'k 0.4'k O.)'} 0.6'k lA'k 0.4'1- o,n 0.6'k 0.4'k 1.2'K- 0.6% 0.3%
1.8'k 6.8'k 1,4'k 4.6'k 2.9'k 2.n 3.1'k 0.4'K- O.4'k 0.5'k 0.5'k 2.4'k 0.3'k 1.9'k 1.8'k 2.n 1.3'K 0.4'k 5.1'k 1.l'K 1.7'k 0.8'k t.3'k 5.1'k 1.4'k 4.3'k 3.4'1- 2.1'k 1.7"7,
1O,6,} 15.1'k 3.1'k 9,7'k 20.8'k 4.1'k 3.5'k 12.n 1O.9'k 5.8'k 8.9'k 5.5'k 6.3"k 6.3'k 4.6'k 22.9'k 7.W 2.4'k 11.5'k 10.3'k 13.1'k 10,9'k 7.8'k 2.W 6.1'k 1O.5'k 11.3'k 9.0'k 5.3"7,
4.6'k O.W 39,n D.O'k 1.5'k 1.8'k 0.0'.< 4.2'k 4.6'k 2.6'k 2.n O.W O.W O.W 26.5'k O.W O.W O.W lo.n 5.5'k 0,0'k 4.2'k 21.4'k 1.5'k O.W 0.0'k O.W S.5% 9.9"7i:
10.7'k 16.8'k 4.2~ 18.9'k 3.2'k 14.4'k 23.3'k 18,6'k 23.2'k 37.W 41.6'1- 32.7~ 28.n O,W 17.W 12.5'k 14,W 28.4'k 7.n 23.9'k 26.0'k 15.5'k 22.8'1- 13.4'k 9.3'k 21.7'k 12.3'k 18.9"7c 10.4'1,
0.1'k 3.6'k 1.3'k 3.5'k 0.1'k O.W 1.4'k 2.2'k 2.5'k 0.1'k o.n O.llk 2.n 2.n 2.1'k 1.9'k 4.W O.W I.W 5.W 2.3'1- o.n 1.I'k 2.4'k 0.8'k O.W 2. I 'K- 1.7'9i: 1.4"k
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3.9'k 3.3'k 2.4'k 6.n 4.8'k- 23.2~ 3.1'k- 8.5';' 1.3'k JAr;. I.n 1.S';' 1.3'k 3.7'k 3.7'k 1.I'k 17.n 1.O'k 10.4'k 6At,;. 4.O'k 3.1'1- 1.1'.f 9.n 0.9'k 10.3'k 14.7<J. 5.2'1, S.5'7,
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O,W O.W 0.O'k O.W 0.0'k 0.1'1- 0,0'k 0.O'k O.W 0.2'k 0.1'1- 0.O'k O.W 0.1'k 0.6'k O.W 0,1'k 0.5~ DA'k 0.1'k 0,1l'} O.O'} O.I'J. 0.O'k 0.O'k O.W 0.2'1- 0.19', 0.2%
0.O'k O.W 0.O'k 0.5'k 2.2,* O.W 0.0'k 0.4Lk O.W O.W 0.1'k o.n 0.O'k 0.4e;. O.W O.W O.W 0,O'k o,n 0.O'k 0,O'k 0,1'k o.n 0.1'k o.n o.n 0.2e;;. 0.2'k 0.5%
0.6'k 0.O'k 0.6'k 2.1'k 2.3'k 0.3'k 0.7'k 4.5'k 1.O'k 0.2'k 0.1'k 2.1'k 1.6<1- 1.5'k 2.79r 3.W 1.I'k O.W 2,8'} o.n 1.5'k 5Alk 2.8'k U'1- 3.8'k 2.3'k 0.9'} 1.6'k 1.4'7,
0.1'l- O.W 0.O'k I.W 0.9'k O.W 4.7,} I.J~ 0.5'k 0.O'k 0.5'k 0.4<;- O.N O.W 0.1'k o.n O.W 0.3'k 0.O'k 0.1'k o.n 0.O'k 1.6'1- 0.2'k 1.7'k 0.O'k' o.n 0.5"7, 1.0'*
0.O'k 0.O'k 0.O'k 0.4'k 0.9'k O.W 0,O'k O.W 0.O'k 0.O'k 0.1'k 0.3'k 0.O'k 0.4<;. O,W 0.O'k 0.1'k O.W O.W 0.O'k 0.4'1- 0.O'k 1.3'k 0.1'l- 0.9'k 0,6'k 1.2'k 0.1'7< 0.3%
1.4'1- 0.O'k 0.3'k 1.O'k o.n 3.4'k 0.7'k 0.3'k 1.8'k 1.4'k 0.9'k 3.4'k lAc;. 1.5'k I.W 0,O'k 1.6'k 0.8'k I.l,} 0.2'k 2.9'k 1.I'k 0.9'k 6.8'k 1.2'k 4A'k 3.n 1.4'l: t.s'7<
0.O'k O.W 0.O'k 0.O'k 0,O'k O.W 0.0'k 0.O'k 0.O'k O.W O.W O.W O.W 0.O'k O.W O.W 0.O'k O.W 0.O'k 0,O'k 0,O'k 0,O'k 0.O'k 0.0'k 0.O'k O.W 0.O'k 0.0'k o.o'k
0.O'k O.W 0.0'} O.W O.W O.W O.W 0.0'l- 0.0'k 0.O'k 0.0'.> O.W 0,O'k 0,O'k 0.O'k O.W O.W O.W 0.O'k O.W 0.0'.> 0.O'k O.W 0.O'k O.W 0.O'k 0.O'k 0.0"k 0.0'7,
15.4'k 0.O'k 0.O'k O.W O.W 0.O'k 0.0'k 0.O'k 5.0'.> 0.O'k O.W 0.O'k O.W O.W 0,0'.> 0.O'k 1.8'k 0.O'k O.W 3.0'.> 0O'k O.W O.W 0.O'k O.W O.W O,W 1.0'7c: 3.3%
O.W 0.0'.> 0.0'} O.W 0.0'.> O.W O.W 0.O'k O.W 0.0'.> O.W O.W 0.0'.> 0.O'k O.W O,W O.W 0.9'k 0.O'k O.W 0,O'k 0.0'k 0,O'k O.W O.W O,W 0.0'k 0.0'k 0.2%
0.0'.> O.W 0.0'.> O.W O.W O.W 0.0'k 0.O'k O.W 0.O'k 0.O'k O.W 0.O'k O.()<K. O.W D.O'k 0.O'k O.W 0.O'k O.W O.W 0.0'k O.W O.W 0.0'.> O.W 0.O'k 0.0% 0.0'7,
O.W 0.O'k 0.0'} 0,O'k 0.0'k 0.O'k 0.O'k 0.0'.> 0,O'k 0.O'k 0.0'.> O.W O.W 0.O'k 0.1'k 2.1'k O.W 0.O'k o.o'k 0,0'.> 1.O'k 0.0'k 0,O'k 2.7'k O,W O.W 00'.> 0.2'7, 0.7'7,
0.0'.> 0,0'.> 0.O'k O.W 0.0'k O.W 0.0'k 0.0'} O.W 0,O'k O.W 0.0'k 0.0'k 0.0c;. 0.0'k 0.O'k 0.0'.> 0.0'k 0.O'k O.W O.W 0.0'k 0.O'k 0.0'k O.Qlk 0.0'} 0.0'k 0.0'k 0.0'7,
100.W 100.W 100.0'k 1OO.W lOO.W 100.0'k 100.0'k 100,0'k loo.O'k 100,0'k 100.0'.> 100.0'k 100.0'k 100.0'.> 1oo.0'k 100.O'k 100,W 100.0'l- loo.O'k 100.0'k lOO.O'k 100,0'.> 100,0'k 100.0'k 100.0'k 100.0'.> IOO.W 100.0'k 0.0'k
Commercial Waste
N ~, ~ ~ ~.
'" '" ~ '" ~ ~ ~ ~
'" '" '" ~ c
~ - - ~ ::: - - :':
~, ~, ~, ~. ~. ~, ~, ~. ~. ~, ~, ~
1.2'k 6.1'k 0.2'k 1.2'K 7.3<;' 1.6'k o.n 0,O'k 0.O'k 2.4'k 6,O'k I.n OAe;. 1.5'1- 2.O'k 0.0'k 0.4'k 2.5'k 0.1'k 9.7'lr- 1.7'k 2.2% 2.7%
3.4'k 17.5'k 32.4'k 3.1'k 13.3'k 15.3'k 11.6'k 18.0'k 29.5'k 11.5'k 26.5'k 14.2'k 5.2'K 13.2'k 16.5'k 15.6'k 17.n 19.6'k 13.n 11.8'k 20.8'k 15.7% 7.59,
0.O'k 0.O'k 4,n D.2e;;. o.n 4.8'k 1.0'k 0.O'k 4.6st O.W 7.8'k 0.3'k O.:{'k 0.O'k 0.O'k o,n O,W O.O'k 0.4\!- 0.O'k 1.6~ 1.2% 2.29,
0,O'k 0.7'k 1.9e;. 0.1'k 2.5'1- 0.5'k 0,1'k 0.O'k 5,n 0.1'k 22.5'k o.n O.~'1- 5.W 0.O'k 0.6'k 0.0'k 2.0'} 0.1'k 0.8'k 0.8ek 2.1'7c: 4.9'7,
5.5'k 45.2lk 18.3'k 8,O'k 45.8'1- 22.0'k 6.n 1O.4'k IIA~ 9.6'k 0.6'k 17.8'k 6.O'k 7.1'k 9.6'k 17.9'k 3.6'k 4.3'k 1.8'k 15.8'k 21.4'k 13.89', 1l.3'7c
o.n 1.3'k O.O'} 0,3'k 0.4'k 0.8'k o.n 0.4'k 0.O'k 0.5'k 0.4'k 0.2'k 1.0'k 0.6'k o.n 0.4'k 1.0'k 1.I'k 0.3'k 0.2'k LO'k 0.59', 0.4%
0.3'k 0.3'k 0.0(;' 0.1'k 1.O'k 0,9'k 0.4'k 0.7'k Oo4'k 0,0'k 0.2'k 0.7'k 0..1'k o.n l.l'k 0.2'k 0.4'k 0.8'k 0.O'k 0.2'k 1.I'k 0.4'7c: 0.4%
O.W OA'J. 0.O'k 0.4'k 0.O'k 3.1'k 0.O'k 0,O'k 0.4'k 0.6'k o.n 0.3'k 0.9'} 1.8'k 5.1'k o.n 0.3'k I.l'k 0.2'k 4.3'1- 1.5'k 1.09', 1.5'k
0.O'k O.W 0.0'} 0.1'k 0.4'k 0.9e;. D.le;;. 0.O'k 0,O'k 0.1'k 3.6'k 0.5'k O.O'k 0.4'k 0.9'k 0.1'k 0,0'k 0,3'k 0.2'k 0.2'} 1.0'k 0.4'7, 0.8%
I
J.I'k 3.5'k 25.8'k 4.3'k 6,n 8.n 2.4'k 0.3'k 7.n 3.1'k o.n 2.3'1- 3.3~ 9.5'k 10.8'k 2.n 5.7'k 504'1- 6.9'k 4.4"1- 4.5'l- 5.7'7, 5.4"7c
0.8'k 0.2'k o.n 1.7'k 2. 1 ',t- 0.8'k 0.6'} 0.6'k 0.7'k 1.5'k 5.0'k 0.O'k OJ'k 0.8'k 1.~'1- 0.6'k 0.3'k 0.9'k 0.4'k 0.9'k 2.O'k 1.0'7, 1.1%
5.2'k 0.4'k 3.1'k 0.9'k 1.0'k 0.8'k 2.2'k 19.5'k 0.4'k 1.2'1- 1.9'k o.n i.8'k 1.9'k 11.6'k 2.7'k 2.8'k 8.3'k 2.3'k 1.1'1- 0.9'k 3..3'7, 4.6"7,
4.n 1O.1'k 0.0'k 59.5'l- 3.5'k 4.2'k 24.7'k 31.4'k 21.6'k 8,8'k 0.0'k 10.3'1- 2.3'k 11.l'k 31.6'k 1.I'k 6,8'k 15.n 0.O'k 26.9'k 31.5'k 14.5% 15.20/,
0.O'k 0.O'k 0.O'k O.W 0.0'k 25.1'k 14,7'k 0.O'k O.W O.W 0.O'k 0.O'k 0.O'k 0.0'k 0.O'k O.W 0.O'k 0.0'k 0,0'k O.OI!- 0.0'k 1.9% 6.2'7c
0,O'k 5.6'k O.W 0.3'i 0.0'k 0.O'k 1.3'k 7.I'k 0.O'k 0.O'k 0.3'k 21.4'k 0,0'k 0,0'k O.W 0.O'k 11.2'k 0.O'k 22.3'k 0.O'k 1.5e;. 3.4% 6.8'k
5.n O.W 5.4'k 5.5'k 0.2'k 4.2'... 0,O'k 4A'k 0.4'k 1.5'k 1.I'k 2.n 13.6'k 5.n o.n 110411- 0.O'k J.n 7.n 0.1'k 0.4'k 3.59t: 3.8'k
0.O'k 0,O'k O.W 0.1l'} 0.2~ 0.5'k 0,0'k O.W 0.O'k 0.2'k 0.4'k O.W ,O.W OA'1- 0.O'k 1.6'k- 0.O'k 0,O'k 0.7'k 6.3c;. 0.O'k 0.59', 1.4%
.
\3.5'k 0.O'k 1.9'k O.I'k 6.5'J- 0.0';' o.n 3.3'k 0.2'k 2.2'k- 1.7'1- 4.2'k 2.9'k 21.1'1- 0.6'k 4.6'1- 7.3'k 9.2'J- 4.3'1 4.5'k 0.O'k 4.2"7c 5.2%
0.O'k IA'k O.W 0.6'l- 2.9'';' 0,O'k 8.5'k O.W 0.0'k o.n 0.1'1- 4.7'1- \.4'1- 0.5'k 0.O'k 0.6'k 0.O'k 504'1- O.W O.W 0.6'1- 1.39', 2.3'7,
30.4'k 0.5';' 1.6'1- 3,9'l- 2.5e;;. 1.7'k- 7.6'J. I.l'k 2.W 3.9'k 4.1'K 6.W 6.7'k 4.5'k 0.4'1- 4.3'k 10.5'k 3.1'k 16,n 0.1'k 1.6'1- 5.4'7, 6.9'7<
2.5'k 4A'J. 1.2'k o.n I.n O.H O.31J. O.4~ 0.9'k 0.O'k 0.8'k 0.3'k 0.4'l- 0.1'k 1.I'k 0.5'k 0.3'k l.l'k 0.5'k OAll- OA'k 0.89', 1.0%
O,R'} o,n O.W O.)'k 0,1l'} 0.1l'} O,I'} O,W 0.2,} 0.2'k O.I'} 0.0';" 10.0'1- 0.5'k 0.1'k a.7e;. 0.2'k 0.O'k 0,1l'} O.OI!- 0.O'k 0.29', 0.1%
10A'l- 0.0'1- o.n 0.1l'} 0.6'k 0,O'k O,W 0.4'k O,W 0.O'k 0.0'k 0.O'k 26. I 'l- .0.O'k 0,1'k O.W 1.2'k 0,O'k 0.O'k O.4'k O.O'} 1.9% 6.O'k
0.4'J. 0.4';' 0.77.- O.)'J. 0.6'k 2.8'}- 2.O'k 0.1e;;. 0.2'k 1.2'k 3.3'1- 2.n 04'k 7.1'1- 0.1'1- 3.1'k '1.9'k- 0.5'k 2.7'k- 7.8'k 1.3'k 1.8'7, 2.1%
11.5'k 0.1l'} 0.O'k l.:i'k-' 0.0'1- 0.9'1- 0.O'k 0.3'k 0.2'k o.n 0.2'k 1.3'k 0O'k 0.8'k 4.S'k 1.8'k o.n 1.8'k 0.4'l- 0.2<;1- 1.6'1- 1.3'7, 2.6'7,
0.O'k 0.O'k a.G'k 0,1l'... 0,1l'} 0.0'k 0,O'k 0.O'k O.W 0.O'k O.O'} O.W O.ll'k 0,O'k 0,O'k O.W 0.O'k 5,O'k 0,0'k 0.1'k 0.1'k 0.2'0/, 1.I'k
O.W 0.O'k OW 0,0'k 0.0'k 0,0'k 0.3'k O.W 0.0'k 0.O'k 10,9'k o,n 06'k 0.O'k 0,O'k 1.O'k 0,O'k 0,O'k 0.0'k 0.O'k 0.5'k 0.7% 2.49f
0.1e;. OA'k 0,O'k 2.4'k 1.2'k 0.0'1- 0.6'k 0.1'k 0.9'k 1.6'k 0.7'k 0.8'k '2.3e;;. 0.3'k 2.O'k I.n 2.n 0.1e;;. 0.1'k I.l'k 1.8'k 1.0'k 0.9"7,
0.O'k 0.O'k 0.9'} 2.5'1- 0.O'k- 0.0'.> 4.6'l- 104'1- 0.0'} 0.2'k 0.1'k 0.O'k 0.5'k 0.O'k 0.2'k 0.O'k 22.N 0.1'k O.W 0.1'k 0.1'k 1.6% 4.9%
O.W 0.O'k O.W 0.O'k O.W O,W O.W O.W 0.O'k 0.O'k O,W 0,0'k ,,'O.W 0.0'.> 0.O'k 0.O'k 1.4'1- 0.O'k 0.O'k 2.O'k 0.O'k 0.2% 0.5%
0.7'k 0.2'k 0.7'k 1.4'k 0.6'k 0.5'k 9.0'.> 0.O'k \3,I'k 0.0'.> 0.5'k 7.3'k :12.0'1- 6.O'k 0,O'k 1.I'k 0.O'k 7.6'k 18.8'k 0.8'k 0.0'.> 4.3'7< 6.5'k
O.W 1.2'k 0.O'k 0.O'k 0.0'k O.W 0.0'.> 0.0'.> 0.0'.> 49.2'k O.W O.W lOW 0.O'k 0,O'k 0.O'k 0.O'k 0.O'k O.W O.l)'} O.W 2.4% 10.7%
0.O'k 0.O'k 0.O'k O.W 0.0'k 0.O'k O.W 0.O'k O.W 0.O'k O.W O.W' '10'k 0.O'k 0.O'k 0.O'k O.l)'} 0.0'k O.W 0.O'k O.W 0.0'7, 0.0'7<
O.W 0.O'k 0.O'k 0.O'k 0.0'k O.W O.W 0,O'k O.W O.W 0.0'.> O.W'. 0.0'.> 0.0'.> 0.O'k 25.1'k O.W 0.O'k 0.O'k 0.0'k 0.O'k 1.2'7c 5.5%
0.O'k 0.O'k O.W 0.O'k O.W 0,O'k 0.O'k 0.O'k 0.0'.> 0.O'k 0.O'k 0.0'k "0.0'.> 0.0'.> O.W 0.O'k 0.8'k 0.O'k 0.O'k 0.0'.> 0.O'k O.O%- 0.2'7,
O.W 0.O'k 0.O'k 0.0'.> O.W O.W O.W O.W 0.0'.> O,W O.W 0.0'.>' Q,W 0,O'k 0.O'k 0.O'k 0.O'k 0.O'k 0.0'.> 0.O'k 0.O'k 0.09, 0.0'0/,
0.O'k 0.O'k 0.0'k 1.3'k '0.O'k 0.O'k O.W O.W O.W 0.O'k o.n O.W 0.0'k 0.O'k 0.O'k O.W 0.5'k 1.0'1- 0.O'k 0.O'k 0.O'k 0.2% 0.4%
0.O'k 0.0'.> 0,0'k 0.0'k 0.0'k 0.O'k 0.O'k 0.O'k O.W O.W 0.O'k 0,0'k O.W 0.O'k O.W 0.O'k 0.O'k 0.O'k O.W 0.O'k 0.0'k 0.0% 0.0'k
100,W 100.W 100.0'k 100.0'k 100.W 100,W 100,0'k 100.0'.> 100.0'.> 100.0'k 100.W 100.0'k IOO.O'k 100.W loo,O'k 100.0'k 100.0'k 100.0'k 100.0'k 100.0'k 100.W 100.0'7, o.o'k
1\
ResidlComm
-: =
~ H
4.4'7, 3.3'k
12.2'7, 6.4%
0.79, 1.6%
2.4'7, 3.6'k
13.0"7c 9.5%
0.5'7, . 0.3'k
0.6'7< 0.5'k
1.0'lc 1.1"7,
0.6"7c 0.79',
5.0% 3.99,
0.8'7, 0.8'7,
2.79', 3.3'7,
11.4% 11.0'k
3.6'" 8.3'k
11.8'k 115'7,
2.4'% 2.9'k
0.7'" t.s'k
5.09, 5.4'7,
2.4'" 3.0'k
5.4'7, S.5'k
0.8% 0.7%
0.2'7, 0.1'k
1.0'" 4.0"7c
1.8'7, 1.6"Ji:
1.3'7, 2.3'k
0.29', 0.7%
0.4'k 1.6"7c
1.4"k 1.2'7<
1.0'k 3.3'k
0.1'k 0.4'k
2.8'k 4.6~
l.0"k 7.1%
0.0'k 0.0'k
1.0'7, 4.3'k
0.0'7< 0.2%
0.09', 0.0%
0.2'k 0.5'7<
0.0"k 0.0'k
lOO.O'k 0.0'k
snl/97
I,
I
I
.;
Newsprint
r-;
I
Corrugated & Kraft Paper
High-Grade Paper
Magazines
Other Paper
I.
PET Bottles
Clear HDPE Containers
Colored HDPE Containers
f'~'
I;
i
Other Plastic Containers
Polyethylene Film
Polystyrene Foam
Other Plastic
Food Waste
Grass Clippings
Leaves I Other Yard Waste
Ii
Clean Wood
Treated Lumber
Textiles, Rubber, & Leather
I.
Disposable Di~pers
Fines
Aluminum Cans
Aluminum Scr~p
IF;
"
Other Non-Ferrous Metal
Tin.Steel & Bimetal Cans
Ferrous Metal
~;
I';
Batteries
Other Glass
Clear Glass Containers
f'~")
Brown Glass Containers
I;
Green Glass Containers
Other
Roofing Materials
,
I',
.'
Metal
Concrete
Bricks
f0
I
Blocks
Gypsum Board & Plaster
White Goods
TOTAL
I:
I:
I rt;
I'
I
SSORT.xLS . ST ^ TImes
Residential Waste
Monday - 5112197
;;
::i
5.89c
9.5%
0.0%
1.7%
9.0%
0.5%
0.9%
0.6%
0.5,.
4.5<;1,
0.8%
3.7,.
9.6%
ILl'"
12.6%
2.1%
2.49'r;
4.0\10
4.5\10
6.5%
0.8\10
0.2%
0.00/0
1.80/0
1.0%
0.0%
0.1%
0.8<;1,
0.3\10
0.1%
0,7<;1,
0.0<;1,
0.0%
3.8'7<
0.0<;1,
0.0%
0.0\10
0.0'7<
100.0%
~
~
~ "8
o
~
c
- ~ ~
~ 8 ~
1.3'7<
2.3<;1,
0.0'7<
1.0<;1,
1.2%
0.3'7<
0.3<;1,
0.2%
0.1'7<
Ll'7<
0.2<;1,
2.1<;1,
4.1'7<
15.8'7<
5.5'7<
1.4\10
2.4\10
1.3<;1-
2.5'7<
1.8%
0.4%
0.1\10
0.1'7<
0.4%
1.4%
#NUM!
0.2<;1-
0.7%
0.4<;1,
0.2%
0.5%
#NUM!
#NUM!
6.3%
#NUM!
#NUM!
#NUM'
#NUM!
Tuesday. 5113/97
c
"
o
:;:
7.29c
9.59c
O.29c
2.5%
12.4%
0.6%
0.6%
Ll%
0.5%
3.9'7<
0.7%
1.4%
9.5%
2.4%
23.0%
1.0<;1,
0.9%
6.30/0
1.5%
5.8'7<
0.8<;1,
0.2<;1,
0.4<;1,
I.7%
0.7<;1,
0.1'7<
0.4<;1,
1.3'7<
Ll<;l,
0.1<;1,
1.3<;1,
0.0<;1,
0.0<;1,
0.7%
0.0%
O.O'7c
0.00/,
0.0'7< #NUM' 100.0% 0.0<;1,
0.0%
1.6<;1,
2.8'7<
0.0<;1,
1.2'7<
1.5<;1,
0.4<;1,
0.4<;1,
0.2<;1,
O.29c
1.30/c
0.3%
2.5<;1,
5.0<;1,
19.2'7<
6.690
1.7%
2.9%
1.6%
3.0\10
2.1%
0.5'7<
0.2'7<
0.1%
0.5'7<
1.7<;1,
0.0%
0.3<;1,
0.9'7<
0.5%
0.2'7<
0.6<;1,
0.0<;1,
0.0%
7.7'7<
0.0%
0.0%
0.0<;1,
0.0'7<
1
c;;8
3.0%
4.0<;1,
0.3<;1,
2.0<;1,
4.1<;1,
0.3<;1,
0.4<;1,
0.8<;1,
0.6'7<
1.4<;1,
0.4%
U<;I,
6.0%
1.6<;1,
13.1<;1,
1.0%
1.6%
7.9%
1.2%
3.5<;1,
0.4%
0.2<;1,
0.4%
1.2<;1,
1.0<;1,
0.1<;1,
0.8<;1,
1.6%
1.6%
0.3<;1,
1.0%
0.0<;1,
0.0<;1,
1.9'7<
0.0<;1,
0.0<;1,
0.0%
0.0<;1,
o
~
;:; -
~!j
2.0%
2.7%
0.2<;1,
1.4<;1,
2.7%
0.2<;1,
0.2%
0.6%
0.4%
0.9%
0.2<;1,
0.8<;1,
4.0%
1.1'7<
8.8%
0.7%
1.0%
5.3%
0.8%
2.3%
0.3<;1,
0.1%
0.3%
0.8%
0.7'7<
0.1%
0.5%
1.1'7<
1.1<;1,
0.2'7<
0.7<;1,
#NUM'
#NUM!
\.3<;1,
#NUM!
#NUM!
#NUM!
#NUM!
0.0%
Wednesday. 5/14/97
"
o
L.
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Thursday - 5/15/97
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5.7%
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~
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0.0<;1,
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Spring Wasle Sampling Event. Statistical Analysis of Percentage Composition
~ .~
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4.89c
4.5%
0.1 %
2.7%
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Event Average
.
.
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6.1%
9.5%
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2.6%
12.4%
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,
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0.7%
4.4%
0.6%
2.2%
9.0%
4.9%
18.4% 10.1%
1.6%
0.8%
5.6%
3.2%
5.3%
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0.2%
0.3%
1.8%
1.3%
0.1%
0.2%
1.7%
0.5%
0..2%
1.6%
0.0%
0.0%
0.9%
0.0%
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0.2%
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3.5%
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0.2%
0.7%
0.2%
0.6%
0.2%
2.3%
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0.3%
0.1%
1.7%
0.5%
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9.5%'
3.0%
3.2%
1.4%
0.4%
1.6%
0.5%
5.6%
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3.3%
1.0%
4.2%
1.3%
0.5%
0.2%
0.2%
0.1%
0.7%
0.2%
0.9%
0.3%
2.2%
0.7%
0.2%
0.0%
0.4%
0.1%
1.4%
0.4%
1.0%
0.3%
0.4%
0.1%
1.5%
0.5%
0.0%
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3.1%
1.0%
0.2%
0.1%
0.0%
#NUM!
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0.0%
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0.0%
100.0% 0.0% #NUM! 100.0% 0.0% #NUM!
Commercial Waste
Monday - 5/12197
c
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2.2'X
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Tuesday - 5/13/97
:j
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1.9<;1,
17.5%
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1.79<
19.3%
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0.79<
0.790
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0.5%
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4.6<;1,
0.0%
0.0%
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0.0<;1,
0.0%
0.0<;1,
100.0<;1, #DIV/O' #DIV/O! 100.0% 0.0<;1,
0.0%
2.6%
13.9%
2.1 %
0.9%
18.2% 21.1<;1,
0.59,
0.29,
0.2%
0.0%
11.1 %
0.6%
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14.390
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0.2%
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2.5%
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8.5%
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0.4%
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#NUM!
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Wednesday - 5/14/97
~
2.4%
14.1%
1.8<;1,
5.7%
8.2<;1,
0.5<;1,
0.39,
0.8<;1,
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4.3%
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5.0%
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2.8%
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0.0%
2.4%
1.2%
0.1%
0.0%
7.2%
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~ .~
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3.4%
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8.3%
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0.0%
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0.3%
0.0<;1,
1.8%
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2.8%
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7.8%
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7.3'7<
18.1'7<
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Thursday. 5/15/97
"
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1.0%
16.6<;1,
0.1<;1,
0.5'7<
7.4'k
0.6<;1,
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6.3'"
0.7%
5.5<;1,
10.990
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6.79r:
4.6'"
0.59',.
5.2\10
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0.2%
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1.9'7<
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5.5'7<
0.0'7<
0.0<;1,
5.0<;1,
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11.2% 8.3<;1, 0.0%
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Friday - 5/16/97
16.3'7<
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18.6<;1,
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11.6%
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0.7'"
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0.0%
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0.4%
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Event Average
"
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2.2%
13.8% 12.3%
0.5%
0.4%
1.0%
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3.3%
14.5%
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3.5'7,
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4.2%
1.3%
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0.8%
0.2%
1.9%
1.8%
1.3%
0.2%
0.7%
1.0%
1.6%
0.2%
4.3%
2.4%
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1.2%
0.0%
0.0%
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1.1%
0.4%
4.6%
1.7%
15.2%
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6.2%
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2.4%
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1.90/.,
2.3%
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6.9%
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1.0%
O.47Cl
0.2%
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6.0%
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0.87.,
2.6%
0.9%
0.4%
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6.5%
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10.7%
3.9%
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5.5%
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0.2%
0.1%
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0.0%
#NUM!
0.0<;1, 100.0% 0.0% #NUM!
Residential/Commercial
Event Average
~
"'E '5 0
~Ci
~ .g~ t:: i:
= .;::: ~ 5 ~
~ ~
:; <J:_ :;:::.u..:
4.4% 3.3% 0.8%
12.2% 6.4% 1.5%
0.7% 1.6% 0.4%
2.4% 3.6% 0.9%
13.0% 9.5% 2.3%
0.5% 0.3% 0.1%
0.6% 0.5% 0.1%
1.0% 1.1% 0.3%
0.6% 0.7% 0-2%
5.0% 3.9% 0.9%
0.8% 0.8% 0.2%
2.7% 3.3% 0.8%
11.4% 11.0% 2.6%
3.6% 8.3% 2.0%
11.8% 11.5% 2.7%
2.4% 2..9% 0.7%
0.7% 1.5% 0.4%
5.0% 5.4% 1.3%
2..4% 3.0% 0.7%
5.4% 5.5% 1.3%
0.8% 0.7% 0.2%
0.2% 0.2% 0.1%
1.0% 4.0% 1.0%
1.8% 1.6% 0.4%
1.3% 2.3% 0.6%
0.2% 0.7% 0-2%
0.4% 1.6% 0.4%
1.4% 1.2% 0.3%
1.0% 3.3% 0.8%
0.2%- 0.4% 0.1%
2.8% 4.6% 1.1%
1.0% 7.1% 1.7%
0.0% 0.0% #NUM!
1.0% 4.3% 1.0%
0.0% 0.2% 0.0%
0.0% 0.0% #NUM!
0.2% 0.5% 0.1%
0.0% 0.0% #NUM!
100.0% 0.0% #NUM!
8121/97