SEPA
United States
Environmental Protection
Agency
EPA-600/R-05/141
October 2005
A CASE STUDY
DEMONSTRATING US EPA
GUIDANCE FOR EVALUATING
LANDFILL GAS EMISSIONS
FROM CLOSED OR ABANDONED
FACILITIES
ROSE HILL REGIONAL LANDFILL
SOUTH KINGSTOWN, RHODE
ISLAND
Rose Rill Rcoclins-Transfer Station
OPERATING HOURS
MONDW-SATUROAY fOOnn. - 3 Ouc
CLOSf.O Sunasys *nd Holid*vs
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EPA-600/R-05/141
October 2005
A CASE STUDY DEMONSTRATING U.S.
EPA GUIDANCE FOR EVALUATING
LANDFILL GAS EMISSIONS FROM
CLOSED OR ABANDONED FACILITIES
ROSE HILL REGIONAL LANDFILL
SOUTH KINGSTOWN, RHODE ISLAND
by
ENVIRONMENTAL QUALITY MANAGEMENT, INC.
Cedar Terrace Office Park, Suite 250
3325 Durham-Chapel Hill Boulevard
Durham, North Carolina 27707-2646
EPA Contract No. 68-C-00-186
Task Order Number 3
EPA Project Officer: Ms. Susan Thomeloe
Office of Research and Development (ORD)
National Risk Management Research Laboratory (NRMRL)
Air Pollution Prevention and Control Division (APPCD)
Research Triangle Park, North Carolina.
U.S. Environmental Protection Agency
Office of Research and Development
Washingtion, DC 20460
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Abstract
This report describes a case study that applies EPA-600/R-05/123—the guidance for conducting air pathway
analyses of landfill gas emissions that are of interest to superfund remedial project managers, on-scene coordina-
tors, facility owners, and potentially responsible parties. The particular site examined for this case study was the
Rose Hill Regional Landfill in South Kingstown, RI. The case study exemplifies the use of the procedures and
tools described in the guidance for evaluating LFG emissions to ambient air. The air pathway analysis is used to
evaluate the inhalation risks to offsite receptors as well as the hazards of both onsite and offsite methane explo-
sions and landfill fires. Landfill gases detected at the site were methane and chemicals of particular concern
(COPCs) that encompassed nonmethane organic compounds, 1,1,1-trichloroethane, benzene, chlorobenzene,
chloroethane, dichlorobenzene, methylene chloride, toluene, trichloroethene, vinyl chloride, and xylenes. The
report includes values of 90th percentile concentration of COPCs and isopleths of the COPC concentrations
overlaid on an aerial photograph of the site.
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Foreword
The U.S. Environmental Protection Agency (EPA) is charged by Congress with protecting the Nation's
land, air, and water resources. Under a mandate of national environmental laws, the Agency strives to
formulate and implement actions leading to a compatible balance between human activities and the
ability of natural systems to support and nurture life. To meet this mandate, EPA's research program is
providing data and technical support for solving environmental problems today and building a science
knowledge base necessary to manage our ecological resources wisely, understand how pollutants
affect our health, and prevent or reduce environmental risks in the future.
The National Risk Management Research Laboratory (NRMRL) is the Agency's center for
investigation of technological and management approaches for preventing and reducing risks from
pollution that threaten human health and the environment. The focus of the Laboratory's research
program is on methods and their cost-effectiveness for prevention and control of pollution to air, land,
water, and subsurface resources; protection of water quality in public water systems; remediation of
contaminated sites, sediments and ground water; prevention and control of indoor air pollution; and
restoration of ecosystems. NRMRL collaborates with both public and private sector partners to foster
technologies that reduce the cost of compliance and to anticipate emerging problems. NRMRLs research
provides solutions to environmental problems by: developing and promoting technologies that protect
and improve the environment; advancing scientific and engineering information to support regulatory
and policy decisions; and providing the technical support and information transfer to ensure
implementation of environmental regulations and strategies at the national, state, and community levels.
This publication has been produced as part of the Laboratory's strategic long-term research plan.
It is published and made available by EPA's Office of Research and Development to assist the user
community and to link researchers with their clients.
Sally Gutierrez, Director
National Risk Management Research Laboratory
in
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EPA Review Notice
This report has been peer and administratively reviewed by the U.S. Environmental Protection Agency and
approved for publication. Mention of trade names or commercial products does not constitute endorsement or
recommendation for use.
This document is available to the public through the National Technical Information Service, Springfield. Vir-
ginia 22161.
Disclaimer
This guidance is intended solely for informational purposes. It cannot be relied upon to create any rights enforce-
able by any party in litigation with the United States. This guidance is directed to EPA personnel; it is not a final
action and does not constitute rulemaking. EPA officials may decide to follow the guidance provided herein, or
they may act at variance with the guidance, based on site-specific circumstances. The guidance may be reviewed
or changed at any time without public notice.
IV
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Table of Contents
Section Page
Abstract ii
Foreword iii
Disclaimer iv
List of Figures vi
List of Tables vii
Acknowledgment viii
Executive Summary ix
1 Demonstration Objectives 1
2 Site Description 3
3 SiteFfistory 5
4 Field Activities and Data Collection 7
4.1 Landfill Surface Screening Analysis 7
4.2 Hot Spot and Homogeneity Determinations 11
4.3 Sampling Activities 11
4.3.1 Landfill Soil Gas Sampling 11
4.3.2 Passive Vent Gas Sampling 15
4.3.3 Perimeter Well Gas Sampling 15
4.3.4 Ambient Air Sampling 15
4.4 Quality Assurance and Data Evaluation 15
4.4.1 Accuracy 15
4.4.2 Precision 16
4.4.3 Completeness 16
5 Estimation of Landfill Gas Emissions 17
5. ILandGEM Modeling of LFG 30
5.2 SCREEN3 Modeling of LFG 31
6 Risk Assessment 33
7 Findings and Conclusions 37
Appendices
A Site Activity Photographs A-l
B Wilcoxon Statistical Analysis B-l
C Laboratory Results C-l
D LandGEM Model Runs D-l
E SCREENS Model Runs E-l
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List of Figures
Figure Page
1 Location and Orientation of the Solid Waste Landfill within the Rose Hill
Regional Landfill Site 4
2 Screening Sampling Node Locations 8
3 Measured Screening Results (ppm) forNMOCs 12
4 Measured Screening Results (ppm) for Methane 13
5 Rose Hill Sampling Locations 14
6 NMOC Concentration Isopleths (ppmvC) from Summa Sampling 18
7 1,1,1 -Trichloroethane Concentration Isopleths (ppbv) from Summa Sampling 19
8 Benzene Concentration Isopleths (ppbv) from Summa Sampling 20
9 Chlorobenzene Concentration Isopleths (ppbv) from Summa Sampling 21
10 Chloroethane Concentration Isopleths (ppbv) from Summa Sampling 22
11 1,4-Dichlorobenzene Concentration Isopleths (ppbv) from Summa Sampling 23
12 Toluene Concentration Isopleths (ppbv) from Summa Sampling 24
13 Trichloroethene Concentration Isopleths (ppbv) from Summa Sampling 25
14 Vinyl Chloride Concentration Isopleths (ppbv) from Summa Sampling 26
15 m,p-Xylene Concentration Isopleths (ppbv) from Summa Sampling 27
16 o-Xylene Concentration Isopleths (ppbv) from Summa Sampling 28
17 Rose Hill's Two Homogeneous Parcels 29
18 NMOC Emission Rates: 1967-2203 31
19 Example LandGEM Model Run Output 32
VI
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List of Tables
Table Page
1 Rose Hill Screening Sample Results 9
2 COPCs Commonly Found in LFG 17
3 Analytical Results for COPCs 30
4 COPCs 90th Percentile Concentrations for Northern and Southern Parcels 30
5 Emission Rates of COPCs by Parcel 31
6 Modeled Maximum Annual Concentrations 32
7 Risk Analysis 33
vii
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Acknowledgement
The following individuals have reviewed this case study and the Fact Sheet or the Guidance for Evaluating
Landfill Gas Emissions from Closed or Abandoned Facilities and made thoughtful suggestions to support the
preparation of the reports: Ed Hathaway (EPA Region 1). Roger Duwart (EPA Region 1). David Healy (Mary-
land Department of Environment), Gary Jablonski (Rhode Island Department of Environmental Management,
Fred MacMillan (EPA Region 3), Craig Mann (Environmental Quality Management , Inc.), Dave Mickunas
(EPA-ERTC), Dave Newton (EPA Region 1). Dan Pazdersky (Harford County Maryland), Bill Rhodes (EPA-
ORD), Tom Robertson (Environmental Quality Management, Inc.), Ken Skahn (EPA-OSWER), Susan Thorneloe
(EPA-ORD), Bob Wright (EPA-ORD).
Vlll
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Executive Summary
The Rose Hill Regional Landfill (Landfill) is located within the town of South Kingstown. Rhode Island in the
village of Peace Dale. This site encompasses approximately 70 acres. The facility is composed of three separate,
inactive, disposal areas, including the solid waste landfill, bulky waste disposal area, and a sewage sludge land-
fill. These areas have been covered with soil and graded and currently support vegetative cover. The Landfill,
which began operation in 1967, is in an abandoned gravel quarry. The Regional Landfill operated as a municipal
disposal facility for the towns of South Kingstown and Narragansett. Industrial waste, however, was also ac-
cepted at the facility during its years of operation. In October 1983, the Regional Landfill reached its state
permitted maximum capacity and ceased active land filling operations. The solid waste landfill located in the
western portion of the site is approximately 28 acres and operated from 1967 until 1982.
On-site groundwater monitoring wells contain several volatile organic compounds (VOCs) including
dichloroethane, chloroethane, vinyl chloride, benzene, and xylenes, as well as some heavy metals. Visual obser-
vations indicate that Mitchell Brook, an unnamed brook, and the Saugatucket River are impacted by contami-
nated run-off from the site. Early investigations determined that landfill gases are migrating laterally off-site in
the vicinity of some residential properties. Three private wells adjacent to the site are contaminated with low
levels of organic compounds, as are on-site soils. The site is not completely fenced, making it possible for people
to come into direct contact with the landfill materials on-site. The Saugatucket Pond, located 2,000 feet down-
stream from the site, is used for fishing and swimming. A freshwater wetland is also located 500 feet downstream
of the site and could be subject to contamination. There were several on- and off-site LFG monitoring wells with
elevated methane levels. The Rose Hill site included: near-by single family homes, institutional buildings, and a
golf course. As a result of this and subsequent investigations, the landfill was placed on the National Priority List
(NPL) on October 4, 1989.
This case study documents how the guidance can be used to evaluate landfill gas emissions. It illustrates the
usefulness of the information, and procedures presented in the Guidance for Evaluating Landfill Gas Emissions
from Closed or Abandoned Facilities (EPA-600/R-05/123). By applying the investigative techniques and recom-
mended practices, the research team was able to:
1 Determine where the landfill gases are escaping into the atmosphere,
2 Identify the chemicals of potential concern,
3 Quantify the speciated LFG emission rates,
4 Identify the most likely to be affected at off-site location(s), and
5 Characterize ambient air concentrations.
This case study report provided data and information that were used by the remedial project manager to:
1 Assess the health risk associated with the emissions from the landfill,
2 Determine if additional site investigation effort is needed,
3 Evaluate the level of effort associated with the existing LFG monitoring program,
4 Determine if the previously proposed remedial design needed to be altered,
5 Evaluate the need for institution controls and future land use policy decisions, and
ix
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A Case Study
6 Decide if the risks and hazards associated with the landfill gas needed to be controlled with LFG control
technology.
Specific to the Rose Hill site the following lessons were learned:
• The conventional field screening, discrete sampling using Sumrna canisters, commercial laboratory analy-
sis using TO 15 analytical methods, and emission and dispersion modeling procedures provided the
information needed to assess the risks and hazards associated with the LFG emissions. The turn-around
time for the commercial laboratory was measured in weeks. The data reduction and modeling efforts
require 2-3 man days of effort. Hence, health risks could not be quantified on a real-time basis. Readily
available equipment and ordinary environmental technician skills are required to obtain quality results.
• The conventional field screening, discrete sampling using Tedlar bags, onsite mobile laboratory using
EPA Method 18 analytical procedures, and emission and dispersion modeling procedures provided the
information needed to assess the risks and hazards associated with the LFG emissions. The onsite mo-
bile laboratory was unable to quantify the COPC's concentrations because of detection limit issues.
• Using the research data, the predicted COPC ambient air concentrations are below that which would
create an unacceptable risk at the 1 * 10"6 level.
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Rose Hill, Rl
Section 1. Demonstration Objectives
The purpose of the activities described in this document 05/123). It was also the intent of this demonstration to
was to provide a demonstration of the procedures described provide an example case study to be included in the guid-
in the Guidance for Evaluating Landfill Gas Emissions from ance for reference by the practitioner. These efforts were
Closed or Abandoned Facilities (Guidance) (EPA-600/R- not intended to provide a comprehensive site analysis or
complete risk assessment.
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A Case Study
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Rose Hill, Rl
Section 2. Site Description
The Rose Hill Regional Landfill (Regional Landfill) is lo-
cated within the town of South Kingstown, Rhode Island
in the village of Peace Dale. The site description contained
in this section was derived from historical literature avail-
able for the site. This site encompasses approximately 70
acres. The facility is composed of three inactive disposal
areas, including the solid waste landfill (28 acres), a bulky
waste disposal area (11 acres), and a sewage sludge land-
fill (unknown). These areas have been covered with soil,
graded, and currently support vegetative cover. An active
transfer station is located on site where municipal refuse is
unloaded from the refuse collection trucks and transferred
to trucks that haul the refuse offsite to a separate landfill
facility owned and operated by the state of Rhode Island.
Figure 1 shows the approximate location and orientation
of the solid waste section of the Regional Landfill.
The facility is situated on the east side of Rose Hill Road
and is bordered by Rose Hill road to the west, the
Saugatucket River to the east, residential property to the
north, and a wooded wetland to the south. Mitchell Brook
flows southerly through the center of the site and joins the
Saugatucket River south of the site. An unnamed brook,
originating on the west side of Rose Hill Road, flows
through the wetland and joins the Saugatucket River 500
feet south of Mitchell Brook.
Residential development has occurred along Broad Rock
Road, 1200 feet east of the site. There has also been con-
siderable development along Rose Hill Road to the north
of the site. A golf course and clubhouse have been con-
structed on the west side of Rose Hill Road, immediately
opposite the facility and to the north of an active sand and
gravel operation.
The town of South Kingstown is primarily a residential
area with limited industry. The University of Rhode Island
(URI), located three miles northwest of the site, houses the
largest population center and provides a major portion of
South Kingstown's employment and business income.
Water supplies in South Kingstown are a mixture of pri-
vate wells and district water supply sources. Supply wells
for two water supply districts, URI and the Kingstown Fire
District, are located within three miles of the facility.
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4.594.
4.594,
4.394
4,593.SOO_
4,594.400
.4,594.200
Bos* nop was photographed on 29 Hor 1995 by the Notional Aerial Photoyophy Progrftn ond d^ftizrfl by
The base nop is projected in Universal Tran«ver«e Hercotor tUTM) Zone 19 on the North Anericon dotix* of 1983.
Figure 1. Location and Orientation of the Solid Waste Landfill within the Rose Hill Regional Landfill Site.
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Rose Hill, Rl
Section 3. Site History
The site history contained in this section was derived from
historical literature available for the site. The Rose Hill
Regional Landfill, which began operation in 1967, is lo-
cated in an abandoned gravel quarry. The Regional Land-
fill operated under an annually renewable state permit from
the Rhode Island Department of Environmental Manage-
ment (RIDEM) for approximately 16 years. The Regional
Landfill operated as a municipal disposal facility for the
towns of South Kingstown and Narragansett. Industrial
waste, however, was also accepted at the facility during its
years of operation. In October 1983, the Regional Landfill
reached its state permitted maximum capacity and ceased
active land filling operations.
As previously mentioned, the Regional Landfill is com-
posed of three disposal areas, none of which are currently
active. The solid waste landfill, located in the western por-
tion of the site, is approximately 28 acres in area, and it
operated from 1967 until 1982. The exact depth of the ex-
cavation where the solid waste landfill exists is unknown,
but it reportedly extended approximately to bedrock in
some places. Refuse was reportedly deposited in areas at,
above, and below the water table. The thickness of solid
waste deposited throughout the landfill prior to 1977 is
unknown. From 1977 to 1982, between 10 and 14 feet of
solid waste was deposited. Borings conducted by C.E.
Maguire, Inc. in 1977 have confirmed the presence of bed-
rock within 2.5 feet of ground surface along the eastern
portion of the solid waste landfill. Borings have indicated
that bedrock was encountered at 31.3 feet on the west side
of the site along Rose Hill Road. From a seismic survey, it
appears that the depth to bedrock along the south of the
solid waste landfill is between 29 and 32 feet below ground
surface. Upon closure, the solid waste landfill was cov-
ered with 0.5 to 2 feet of sandy soil and subsoil and seeded.
The sewage sludge disposal area is located in the northeast
section of the site between Mitchell Brook and the
Saugatucket River. No surveys of the sewage sludge land-
fill have been conducted to determine its size. This area
operated from 1977 to 1983. Sludge was received from the
South Kingstown wastewater treatment plant and areas
throughout the state of Rhode Island and deposited in
trenches. The depth of excavation of the trenches is un-
known. Problems with the high moisture content of the
sludge persisted throughout the operation of this area and
prompted the town of South Kingstown to initiate the haul-
ing of sludge to the Johnston Landfill. Currently, the sew-
age sludge landfill is covered with soil, graded, and seeded.
The bulky waste disposal area was proposed as an 11-acre
area that is located west of the solid waste landfill and south-
west of the sewage sludge landfill. This area is approxi-
mately 200 feet east of Mitchell Brook and 250 feet west
of the Saugatucket River. Disposal of bulky waste began
in this area in 1978. Solid waste was also disposed in the
interim period between closure of the solid waste area and
construction of the transfer station, May 1982 through
October 1983. This area was covered, graded, and seeded
in the same manner as the solid waste landfill.
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A Case Study
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Rose Hill, Rl
Section 4. Field Activities and Data Collection
Field activities were conducted at the Rose Hill Regional
Landfill, located in South Kingstown, Rhode Island, from
July 22, 2002 through July 25, 2002. Field activities in-
cluded landfill surface screening analysis, screening data
reduction, hot spot and homogeneity determinations, land-
fill soil gas sampling, passive vent gas sampling, perim-
eter well gas sampling, and ambient air sampling. Pictures
from the site activities can be found in Appendix A.
Prior to arrival at the site, the U.S. Environmental Protec-
tion Agency (EPA) Remedial Project Manager (RPM) no-
tified the immediate surrounding residences and businesses
that an assessment was to be conducted on and around the
landfill area. This was part of a public relations effort to
notify the public and address any concerns prior to the ac-
tivities taking place.
To assist with the field activities, a 30 m by 30 m sampling
grid was developed across the extent of the landfill area
prior to the field activities. This sampling grid was devel-
oped to include the entire extent of the landfill boundary
area and extend 30 m beyond that boundary area. This grid
was then numbered for each node location, forming a ser-
pentine sampling pathway across the grid. A total of 190
sampling locations comprised the sampling grid layout
developed for this site. A reference point was identified
using an identifiable landmark on the site to locate the start-
ing point. Figure 2 shows the grid and pathway used for
the screening analysis.
4.1 Landfill Surface Screening Analy-
sis
As soon as personnel were on site, the reference point was
visually located, and using a handheld global positioning
system (GPS), the starting point (Node No. 1) was located
to begin the screening analysis. The screening analysis in-
cluded measurements for non-methane organic compounds
(NMOCs) using a photo ionized detector (PID) and for
methane (CH4) using a flame ionized detector (FID). Both
the PID and FID were held no more than one inch above
the ground while measurements were being made. It should
be noted that the field instrumentation was very sensitive
and drifted quite significantly due to slight gusts of wind
across the landfill cover. Readings were taken for approxi-
mately one minute, and the average value excluding the
extreme highs and lows were recorded. While conducting
the serpentine walk across the site, an effort was made to
identify areas containing cracks and gaps in the landfill
cover, and measurements were made at these locations to
the extent possible. All predetermined sampling locations
were not accessible for a variety of reasons ranging from
being located on private property to being inaccessible by
the field crew due to extreme overgrowth. An attempt was
made to collect a reading at each location, with measure-
ments being collected not greater than 10m from the pre-
determined locations. If it was necessary to skip a location
due to inaccessibility within the acceptable 10 m range,
then replicate readings were collected at the next acces-
sible location. These replicate readings were intended to
provide for additional quality assurance and quality con-
trol (QA and QC) data and were not intended to back fill
missing data for an inaccessible node. Duplicate readings
were also taken at predefined locations as part of QA and
QC efforts. These predetermined locations were selected
based on a random number generator. All screening data
were recorded on field log data collection forms along with
any field notes relevant to specific locations. There was 89
percent data collection efficiency. Table 1 provides the
screening sample results.
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Rose Hill Landfil
Kingstown, Rl
Sampling grid is
30 m by 30 m
ENVIRONMENTAL QUALITY MANAGEMENT, INC.
33SS DLRHAM-CMAPEL KILL HXLCVARD. SUITE 230
DURH*H, MKTH CAROLINA 27707
(919J 4S9-K99 F*X' (919) 4OT-5335
ROSE HILL LANDFILL
Figure 2. Sonpling Locations
South Kingstown, Rhode Island
B 030177,0003
Figure 2. Screening Sampling Node Locations.
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Rose Hill, Rl
Table 1. Rose Hill Screenin
Nod Sample ID No.
1 LFSG-02-07 22 02 -R 001
2 LFSG-02-07 22 02 -R 002
3 LFSG-02-07 22 02 -R 003
4 LFSG-02-07 22 02 -R 004
5 LFSG-02-07 22 02 -R 005
6 LFSG-02-07 22 02 -R 006
7 LFSG-02-07 22 02 -R 007
8 LFSG-02-07 22 02 -R 008
9 LFSG-02-07 22 02 -R 009
10 LFSG-02-07 22 02 -R 010
11 LFSG-02-07 22 02 -R Oil
12 LFSG-02-07 22 02 -D 001
13 LFSG-02-07 22 02 -D 002
14 LFSG-02-07 22 02 -R 01 2
15 LFSG-02-07 22 02 -R 013
16 LFSG-02-07 22 02 -R 014
17 LFSG-02-07 22 02 -R015
18 LFSG-02-07 22 02 -R 01 6
19 LFSG-02-07 22 02 -R 017
20 LFSG-02-07 22 02 -R 018
21 LFSG-02-07 22 02 -R 019
22 LFSG-02-07 22 02 -R 020
23 LFSG-02-07 22 02 -R 021
24 LFSG-02-07 22 02 -R 022
25 LFSG-02-07 22 02 -R 023
26 LFSG-02-07 22 02 -R 024
27 LFSG-02-07 22 02 -R 025
28 LFSG-02-07 22 02 -D 003
29 LFSG-02-07 22 02 -D 004
30 LFSG-02-07 22 02 -R 026
31 LFSG-02-07 22 02 -R 027
32 LFSG-02-07 22 02 -R 028
33 LFSG-02-07 22 02 -R 029
34 LFSG-02-07 22 02 -R 030
35 LFSG-02-07 22 02 -R 031
36 LFSG-02-07 22 02 -R 032
37 LFSG-02-07 22 02 -R 033
38 LFSG-02-07 22 02 -R 034
39 LFSG-02-07 22 02 -R 035
40 LFSG-02-07 22 02 -R 036
41 LFSG-02-07 22 02 -R 037
42 LFSG-02-07 22 02 -R 038
43 LFSG-02-07 22 02 -R 039
44 LFSG-02-07 22 02 -R 040
45 LFSG-02-07 22 02 -R 041
* ND = not detected
b NA = not available
g Sample Result:
Actual UTM
Coordinates '
Easting Northing
291648
291659
291686
291719
291742
291773
291744
291714
291683
291656
291645
NA
NA
291634
291657
291684
291712
291745
291778
291803
291808
291782
291742
291710
291681
291654
291628
NA
NA
291619
291654
291684
291716
291747
291775
291805
291835
291860
291799
291778
291744
291714
291683
291653
291619
4593806
4593806
4593802
4593807
4593813
4591773
4593836
4593835
4593833
4593829
4593834
NA
NA
4593867
4593862
4593866
4593865
4593865
4593862
4593861
4593862
4593896
4593902
4593903
4593899
4593897
4593896
NA
NA
4593926
4593929
4593927
4593918
4593924
4593926
4593925
4593920
4593955
4593952
4593961
4593958
4593957
4593956
4593955
4593954
3.
NMOC
Cone.
0.20
0.43
0.20
0.20
0.20
ND
0.20
0.20
1.80
0.40
ND
NA
NA
ND
0.30
0.60
ND
ND
0.26
ND
ND
ND
ND
ND
0.20
ND
ND
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
: CH4
Cone.
ND
ND
ND
ND
ND
ND
ND
1.00
ND
ND
ND
NA
NA
ND
25.00
ND
ND
300.00
350.00
ND
ND
ND
ND
ND
ND
2.10
ND
NA
NA
ND
3.00
ND
ND
ND
ND
ND
ND
ND
6.00
ND
42.00
2.00
ND
9.00
ND
Table 1. Rose Hill Screeniru
^d Sample ID No.
46
47
48
49
50
51
52
53
54
55
56
57
58
59
60
61
62
63
64
65
66
67
68
69
70
71
72
73
74
75
76
77
78
79
80
81
82
83
84
85
86
87
88
89
90
'ND
bNA
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
LFSG-02-07 22
= not detected
= riot available
02 -R042
02 -R 043
02 -R045
02 -R045
02 -R046
02 -R047
02 -R048
02 -R049
02 -R 050
02 -R051
02 -R052
02 -R 053
02 -R054
02 -R 055
02 -R056
02 -R057
02 -R058
02 -R059
02 -R060
02 -R061
02 -R062
02 -R 063
02 -R064
02 -R 065
02 -R066
02 -R067
02 -R068
02 -R 069
02 -R 070
02 -R071
02 -R072
02 -R 073
02 -R074
02 -R 075
02 -R076
02 -R077
02 -R078
02 -R079
02 -R 080
02 -R 081
02 -D 008
02 -D 009
02 -R 082
02 -R 083
02 -R 084
3 Sample Results
Actual UTM
Coordinates '
Easting Northing
291592
291595
291624
291654
291687
291714
291746
291775
291806
291811
291834
291802
291773
291741
291713
291683
291653
291627
291590
291563
291597
291626
291658
291686
291715
291747
291775
291805
291835
291868
291872
291833
291800
291776
291741
291713
291682
291654
291625
291593
NA
NA
291577
291597
291614
4593944
4593988
4593994
4593986
4593985
4593988
4593984
4593986
4593987
4593988
4594017
4594019
4594016
4594017
4594015
4594016
4594016
4594015
4594019
4594047
4594044
4594049
4594044
4594046
4594045
4594046
4594043
4594045
4594043
4594038
4594067
4594074
4594078
4594074
4594075
4594075
4594074
4594076
4594073
4594076
NA
NA
4594105
4594116
4594103
(continued).
NJMOC CH4
Cone. Cone.
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NA
NA
ND
ND
ND
ND
ND
8.00
ND
ND
ND
ND
ND
12.00
ND
ND
ND
ND
ND
ND
ND
ND
110.00
ND
ND
ND
6.00
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
3.00
ND
NA
NA
ND
ND
1.20
continued
continued
-------
A Case Study
Table 1. Rose Hill Screenini
ivjj* Sample ID No.
91 LFSG-02-07 22 02 -R 085
92 LFSG-02-07 22 02 -R 086
93 LFSG-02-07 22 02 -R 087
94 LFSG-02-07 22 02 -R 088
95 LFSG-02-07 22 02 -R 089
96 LFSG-02-07 22 02 -R 090
97 LFSG-02-07 22 02 -R 091
98 LFSG-02-07 22 02 -D 010
99 LFSG-02-07 22 02 -D Oil
100 LFSG-02-07 22 02 -R 092
101 LFSG-02-07 22 02 -R 093
102 LFSG-02-07 22 02 -R 094
103 LFSG-02-07 22 02 -R 095
104 LFSG-02-07 22 02 -R 096
105 LFSG-02-07 22 02 -R 097
106 LFSG-02-07 22 02 -R 098
107 LFSG-02-07 22 02 -R 099
108 LFSG-02-07 22 02 -R 100
109 LFSG-02-07 22 02 -R 101
110 LFSG-02-07 22 02 -D 012
111 LFSG-02-07 22 02 -D 013
112 LFSG-02-07 22 02 -R 102
113 LFSG-02-07 22 02 -R 103
114 LFSG-02-07 22 02 -R 104
115 LFSG-02-07 22 02 -R 105
116 LFSG-02-07 22 02 -R 106
117 LFSG-02-07 22 02 -R 107
118 LFSG-02-07 22 02 -R 108
119 LFSG-02-07 22 02 -R 109
120 LFSG-02-07 22 02 -R 110
121 LFSG-02-07 22 02 -R 111
122 LFSG-02-07 22 02 -R 112
123 LFSG-02-07 22 02 -D 015
124 LFSG-02-07 22 02 -R 113
125 LFSG-02-07 22 02 -R 114
126 LFSG-02-07 22 02 -R115
127 LFSG-02-07 22 02 -R 116
128 LFSG-02-07 22 02 -R 117
129 LFSG-02-07 22 02 -R 118
130 LFSG-02-07 22 02 -R 119
131 LFSG-02-07 22 02 -R 120
132 LFSG-02-07 22 02 -R 121
133 LFSG-02-07 22 02 -R 122
134 LFSG-02-07 22 02 -R 123
135 LFSG-02-07 23 02 -R 036
* ND = not detected
b NA = not available
3 Sample Results
Actual UTM
Coordinates '
Easting Northing
291654
291685
291714
291746
291772
291805
291815
NA
NA
291825
291789
291770
291744
291713
291683
291652
291624
291594
291583
NA
NA
291571
291605
291627
291656
291686
291715
291737
291768
291805
291835
291869
NA
291821
291802
291770
291743
291714
291683
291643
291623
291595
291567
291561
291555
4594108
4594105
4594106
4594107
4594105
4594107
4594105
NA
NA
4594136
4594135
4594136
4594135
4594136
4594136
4594137
4594137
4594135
4594136
NA
NA
4594167
4594165
4594167
4594166
4594167
4594167
4594165
4594176
4594169
4594163
4594165
NA
4594198
4594196
4594189
4594195
4594197
4594197
4594197
4594197
4594194
4594194
4594190
4594324
(conti
NMOC
Cone.
ND
ND
ND
ND
ND
ND
ND
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NA
ND
ND
ND
ND
ND
0.25
ND
ND
ND
ND
ND
ND
nued).
: CH4
Cone.
ND
ND
ND
ND
ND
ND
ND
NA
NA
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
N
NA
ND
20.00
1.00
ND
ND
1.00
ND
2.00
ND
ND
ND
NA
ND
ND
11.00
1.00
1.00
0.03
2.00
7.00
16.00
ND
ND
ND
Tabl
No.
136
137
138
139
140
141
142
143
144
145
146
147
148
149
150
151
152
153
154
155
156
157
158
159
160
161
162
163
164
165
166
167
168
169
170
171
172
173
174
175
176
177
178
179
180
"ND
11 NA
e 1 . Rose h
Samplc
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
•I ill Screenini
; ID No.
23 02 -R 037
23 02 -R 001
23 02 -R 002
23 02 -R 003
23 02 -R 004
23 02 -R 005
23 02 -R 006
23 02 -R 007
23 02 -R 008
23 02 -D 002
23 02 -D 003
23 02 -R 009
2302 -R010
2302 -R011
2302 -R012
2302 -R013
2302 -R014
2302 -R015
2302 -R016
2302 -R017
23 02 -D 004
23 02 -R 038
2302 -R039
23 02 -D 005
23 02 -D 006
2302 -R018
2302 -R019
23 02 -R 020
2302 -R021
23 02 -R 022
2302 -R023
23 02 -R 024
23 02 -R 025
23 02 -D 007
23 02 -D 008
23 02 -R 026
23 02 -R 027
23 02 -R 028
2302 -R029
23 02 -R 030
23 02 -R 031
23 02 -R 032
2302 -R033
23 02 -R 034
23 02 -R 035
3 Sample Results
Actual UTM
Coordinates '
Easting Northing
291559
291603
291625
291655
291684
291715
291746
291775
291793
NA
NA
291788
291734
291712
291692
291668
291641
291616
291603
291595
NA
291534
291538
NA
NA
291573
291594
291625
291656
291676
291694
291745
291751
NA
NA
291813
291807
291788
291746
291716
291677
291654
291623
291594
291582
4594324
4594217
4594227
4594225
4594226
4594227
4594226
4594227
4594227
NA
NA
4594261
4594262
4594254
4594250
4594253
4594252
4594253
4594257
4594254
NA
4594356
4594357
NA
NA
4594284
4594288
4594286
4594288
4594286
4594294
4594284
4594294
NA
NA
4594311
4594311
4594308
4594334
4594331
4594321
4594316
4594316
4594316
4594317
i (continued).
NMOC CH4
Cone. Cone.
ND
2.50
0.50
5.00
ND
ND
ND
2.00
ND
NA
NA
ND
2.00
ND
ND
ND
ND
ND
ND
ND
NA
ND
ND
NA
NA
ND
ND
1.00
ND
ND
ND
ND
ND
NA
NA
ND
ND
ND
ND
ND
2.00
ND
ND
1.00
1.00
ND
160.00
2.00
20.00
1.00
ND
ND
ND
ND
NA
NA
ND
ND
ND
ND
1 1 .00
ND
ND
12.00
1.50
NA
ND
ND
NA
NA
25.00
130.00
ND
ND
ND
ND
ND
ND
NA
NA
1.00
ND
2.00
8.00
13.00
2.00
1.50
2.00
1.00
7.00
= not detected
= not available
continued
continued
10
-------
Rose Hill, Rl
Table 1. Rose Hill Screening Sample Results (concluded).
§J* Sample ID No.
181
182
183
184
185
186
187
188
189
190
LFSG-02-07
23
LFSG-02-0723
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
LFSG-02-07
23
23
23
23
23
23
23
23
02
02
02
02
02
02
02
02
02
02
-D
-D
-D
-D
-R
-R
-R
-R
-R
-R
010
Oil
012
013
040
041
042
043
044
045
Actual UTM
Coordinates '
Easting Northing
NA
NA
NA
NA
291563
291595
291625
291655
291684
291715
NA
NA
NA
NA
4594338
4594344
4594343
4594343
4594344
4594342
NfMOC
Cone.
NA
NA
NA
NA
ND
ND
ND
ND
ND
ND
: CH4
Cone.
NA
NA
NA
NA
ND
1.00
ND
2.00
2.00
1.00
tioned earlier, for the purposes of this statistical analysis
all non-detect, replicate, and duplicate measurements were
excluded from this analysis.
" ND = not detected
b NA= not available
4.2 Hot Spot and Homogeneity Deter-
minations
The screening data collected were used for two analyses.
The first was for a hot spot analysis. This was accomplished
by importing the screening data set into a graphical con-
touring software package (Surfer) to produce concentra-
tion contours that were layered over an aerial photographic
image of the site. This method allowed for a visual deter-
mination of where the higher concentrations were recorded
during the screening analysis. This method also allowed
the data set to be divided into two data sets based on the
contours derived from these data. This population division
was used as part of the homogeneity determinations. Fig-
ures 3 and 4 show the concentration contours for NMOCs
and methane, respectively.
The second analysis provided a determination of the ho-
mogeneity of the site. This was accomplished through sta-
tistical means by using the Wilcoxon Rank Sum statistical
method, which determines whether two data sets are sta-
tistically similar. If the two sets are similar, then the two
populations are determined to be one nearly homogeneous
area. If the two data sets are determined not to be statisti-
cally similar, then the two sets are said to be two non-ho-
mogeneous areas. To accomplish this task, the hot spot
analysis was used to determine if there appeared to be two
distinct population sets. For this site, the Wilcoxon method
showed that the site has two nearly homogeneous areas.
Appendix B contains the Wilcoxon data analysis. As men-
4.3 Sampling
Sampling activities encompassed sampling landfill soil gas,
passive vent gas, perimeter well gas, and ambient air. Fig-
ure 5 shows all sampled locations. Each of these sampling
methods will be discussed further in the following sections.
4.3.1 Landfill Soil Gas Sampling
As part of this demonstration, landfill soil gas samples were
collected for the chemicals of potential concern (COPCs)
by two methods. The first set of samples were collected
using Summa canisters, which were sent to an off-site com-
mercial laboratory for analysis. The second set of samples
were collected using Tedlar bags and were analyzed at an
on-site laboratory provided by EPAs Environmental Re-
sponse Team Center (ERTC). Field instrumentation was
used at each of the designated sampling locations. These
instruments were used to measure fixed gases carbon di-
oxide (CO2), nitrogen (N2), and oxygen (O2), which were
used to verify that landfill gas (LFG) was being collected.
Sampling was conducted using a slam-bar to drive a sam-
pling hole through the landfill cover, a sampling probe was
inserted into the landfill area, and the hole was sealed
around the probe to minimize ambient air inleakage.
Based on the data analysis conducted, it was determined
that this site consisted of two homogeneous areas. It was
determined that, for purposes of this demonstration, six
Tedlar bag samples would be collected, three samples in
each homogenous area. Samples were collected at grid node
locations with the highest NMOC concentrations (2, 9,16,
137,139, and 148). Summa canister samples were also col-
lected at each of the six node locations. In conducting the
field measurements for fixed gases at node No. 2 it was
observed that the O2 content was greater than 18 percent
and the N2 concentration was greater than 20 percent, indi-
cating the absence of landfill gas in the sample. It was de-
termined that high NMOC reading during screening could
have been attributed to vehicle exhaust and not LFG due
to the close proximity of a road to this location. It was
therefore determined that this sampling location should be
abandoned to prevent sampling interference. The sampling
location was moved to the next highest screening concen-
tration found at grid No. 15. Laboratory analytical results
can be found in Appendix C.
11
-------
INJ
4594401
4594350
4594300
4594250
4594200
4594150
4594100
4594050
4594000
4593950
4593900
4593850
4593800
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
O
09
Figure 3. Measured Screening Results (ppm) for NMOCs.
-------
45944
45
3J
O
CO
CD
4593800
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
Figure 4. Measured Screening Results (ppm) for Methane.
-------
Ambient Air
Sampling Location
Perimeter Well
Sampling Location
Landfill Gas (Slainbar)
Sampling Location
4594050
4594000
4593950
4593900
4593850
4593800
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
O
09
Figure 5. Rose Hill Sampling Locations.
-------
Rose Hill, Rl
4.3.2 Passive Vent Gas Sampling
During the screening analysis of the site, it was observed
that gas monitoring wells were installed within the interior
of the landfill boundary area at grid Nos. 80, 131, and 140.
Because these wells were not properly capped or sealed,
they were assumed to be acting as passive vents through
the landfill cover, and it was decided that these passive
vent areas should also be sampled for further demonstra-
tion purposes. Sampling was conducted using a slam-bar
to drive a sampling hole near the passive vents and through
the landfill cover. A sampling probe was then inserted into
the landfill, and the hole was sealed around the probe to
minimize ambient air in-leakage. Summa canister samples
were collected for COPCs and fixed gases, and Tedlar bag
samples were collected for COPCs. Fixed Gases were also
analyzed at these locations using field instrumentation.
Laboratory analytical results can be found in Appendix C.
4.3.3 Perimeter Well Gas Sampling
The guidance recommends that sampling be conducted at
perimeter wells located nearest to the hot spots and the
closest off-site receptor. For this site demonstration, sam-
pling was conducted at three perimeter wells that were lo-
cated in close proximity to off-site residential houses. At
each of these locations, Summa canisters and Tedlar bags
were used to collect the samples for COPCs and fixed gases
analyses. The Summa canister sampling rate was set to ap-
proximately 0.1 L/min in order to minimize the potential
for ambient air leakage. The Tedlar bag samples were col-
lected at approximately 1.0 L/min. Laboratory analytical
results can be found in Appendix C.
4,3.4 Ambient Air Sampling
As recommended by the guidance, sampling of ambient
air should be conducted at the location where the highest
NMOC concentrations were measured. For the purpose of
this demonstration, samples were collected at grid nodes 9
and 137 using a Summa canister. It should be noted that
the sample taken at node 9 was located directly next to a
storm drain that appeared to be acting as a passive vent
from field observations. An ambient air sample was also
collected at one perimeter well (node 137) that was deter-
mined to be closest to the nearest occupied structure and
and that had the highest NMOC concentration observed
on-site during the screening analysis. Laboratory analyti-
cal results can be found in Appendix C.
4,4 Quality Assurance and Data
The primary purpose of this project is to establish the use-
fulness of the guidance document and identify areas that
need to be clarified or expanded. The field efforts are a
means to collect the information needed to implement the
procedures included in the guidance. A secondary purpose
of the project is to provide the RPMs with information that
will allow them to determine if LFG controls are needed
and if compliance with applicable relevant and appropri-
ate requirements (ARARs) has been achieved. Data qual-
ity objectives are a starting point of an interactive process,
and they do not necessarily constitute definitive rules for
accepting or rejecting results. The measurement quality ob-
jectives have been defined in terms of standard methods
with accuracy, precision, and completeness goals.
Uncertainty associated with the measurement data is ex-
pressed in terms of accuracy and precision. The accuracy
of a single value contains both the measurement's random
error component and the systematic error, or bias. Accu-
racy thus reflects the total error for a given measurement.
Precision values represent a measure of only the random
variability for replicate measurements. In general, the pur-
pose of calibration is to eliminate bias, although inefficient
analyte recovery or matrix interferences can contribute to
sample bias, which is typically assessed by analyzing ma-
trix spike samples. At very low levels, blank effects (con-
tamination or other artifacts) can also contribute to low-
level bias. The potential for bias is evaluated by method
blanks. Instrument bias is evaluated by using control
samples.
4.4.1 Accuracy
Accuracy of laboratory results has been assessed for com-
pliance with the established QC criteria using the analyti-
cal results of method blanks, reagent or preparation blank,
matrix spike and matrix spike duplicate samples, and field
blanks. The percent recovery (%R) of matrix spike samples
is calculated using
%R=—-xlOO
Where A = the analyte concentration determined experi-
mentally from the spiked sample,
B = the background level determined by a sepa-
rate analysis of the unspiked sample, and
C = the amount of the spike added.
The laboratory did not detect any of the analytes in any
sample blanks. The minimum and maximum recovery for
the entire set of laboratory control samples (LCS) was
greater than 70 percent and less than 122 percent. The 4-
bromofluorobenzene surrogate spike recovery was outside
15
-------
A Case Study
of the upper range for 10 out of 20 field samples. The maxi-
mum 4-bromofluorobenzene surrogate spike recovery was
363 percent. The high 4-bromofluorobenzene surrogate re-
covery is indicative of matrix interference, and the results
may be biased on the high side. All other spike surrogate
recovery values were within the target range of 70 to 130
percent.
4.4.2 Precision
The analytical results between matrix spike and matrix
spike duplicate (MS and MSB) analyses for each COPC
have been assessed. The relative percent difference (RPD)
was calculated for each pair of duplicate analysis using
RPD =
S-D
(S+D)/2
x 100
Where S = first sample value (original or MS value) and
D= second sample value (duplicate or MSB value).
Except for methylene chloride and acetone in the dupli-
cate ambient air samples, the RPD for each of the matched
sample pairs ranged from 2.15 to -13.33 percent. The labo-
ratory reported concentrations of methylene chloride and
acetone in one of the duplicate ambient air samples but not
in the other. The calculated RPD for methylene chloride
and acetone in the ambient air samples was 40 and -129.67
percent, respectively. The RPD for the blind reference stan-
dard ranged from 0 to 148 percent. The laboratory reported
concentrations for methylene chloride, acetone, and tolu-
ene in the blind reference standard. The reported values
for the blind reference standard are less than five times the
method detection limit (MDL) for each of the contami-
nants. These three contaminants were not expected to be
in the blind reference standard. The RPD for the labora-
tory control samples (LCS) ranged from 0 to 18 percent.
The calculated RPD for each LCS analyte was less than 5
percent except for 1,2,4-trichlorobenzene and hexa-
chlorobutadiene.
This narrow range indicates that the laboratory was ca-
pable of reproducing the analytical results. Although, nei-
ther methylene chloride, hexane, nor acetone was found in
the associated laboratory blanks, they are common labora-
tory contaminants.
4,4,3 Completeness
Completeness is a measure of the amount of valid data
obtained from a measurement system compared to the
amount that was expected under normal conditions. The
sampling and analytical goal for completeness is 80 per-
cent or more for all samples tested. The percent complete-
ness was calculated by using
Completeness(%) =
(tmmher of valid data)
( number of samples collected \
\ for each parameter analyzed)
xlOO
Ninety three percent of the targeted data was collected and
validated.
16
-------
Rose Hill, Rl
Section 5. Estimation of Landfill Gas Emissions
After all samples were collected, it was possible to esti-
mate the air impact of this site through the methods de-
scribed in the guidance. For the purpose of this demon-
stration, it was determined that only select COPCs com-
monly found in LFG would be fully characterized. Table 2
provides a list of those COPCs commonly found in LFG
and considered in this demonstration. From previous site
activities and visual inspection of concentration isopleths
generated from the laboratory results, the data were di-
vided into groups according to the associated homogenous
areas (parcels) for analysis. Those COPCs that contained
nondetect data were eliminated from further investigation.
Figures 6 through 16 show the soil gas concentration isop-
leths of all COPCs with detected concentrations. These fig-
ures provided a visual presentation of the laboratory re-
sults that were used to further understand the dynamics of
this landfill and to quantify the division of the landfill into
two homogenous parcels, which are shown in Figure 17.
Table 3 provides the analytical results for the northern and
southern parcels of the landfill. The data for each parcel
were analyzed, and the 90th percentile concentrations were
determined using the percentile function of Microsoft Ex-
cel. A percentile is a value on a scale of 0 to 100 that indi-
cates the percent of a distribution that is equal to or less
than the value Table 4 provides the 90th percentile values
of the COPCs for both of the landfill's parcels.
Table 2. COPCs Commonly Found in LFGa'b
1,1,1-Trichloroethane (methyl chloroform)
1,1-Dichloroethene (vinylidene chloride)
1,2-Dichloroethane (ethylene dichloride)
Acrylonitrile
Benzene
Carbon Tetracliloride
Chlorobenzene
Chloroethane (ethyl chloride)
C hlorofluorocarbons
Chloroform
Diclilorobenzene
Ethylene Dibromide
Hydrogen Sulfide
Mercury
Methylene C lib ride
Percliloroelhylene (tetracliloroethylene)
Toluene
Trichloroethylene (trichloroethene)
Vinyl Clibride
Xylenes
a Constituents associated with carcinogenic and chronic
noncarcinogenic health effects that are routinely measured
b Source: EPA, 1997
17
-------
oo
4594400
4594350
4594300
4594250
4594200
4594150
4594100
4594050
4594000
4593950
4593900
4593850
•^^V "•» n II Mr
4593800
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
o
Q>
CO
(D
Figure 6. NMOC Concentration Isopleths (ppmvC) from Summa Sampling.
-------
CO
4594400
4594350
4594300
4594250
4594200
4594150
4594100
4594050
4594000
4593950
4593900
4593850
4593800 •
70
o
v>
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
Figure 7.1,1,1-Trichloroethane Concentration Isopleths (ppbv) from Summa Sampling.
-------
INJ
o
4594401
4594350
4594300
4594250
4594200
4594150
4594100
4594050
4594000
4593950
4593900
4593850
4593800
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
O
09
Figure 8. Benzene Concentration Isopleths (ppbv) from Summa Sampling.
-------
CVS
4594400
4594350
4594300
4594250
4594200
4594150
4594100
4594050
4594000
4593950
4593900
4593850
4593BOQ I
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291900 291S50 291900 291950 292000
3J
O
CO
CD
Figure 9. Chlorobenzene Concentration Isopleths (ppbv) from Summa Sampling.
-------
INJ
INJ
4594401
4594350
4594300
4594250
4594200
4594150
4594100
4594050
4594000
4593950
4593900
4593850
4593800
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
O
09
Figure 10. Chloroethane Concentration Isopleths (ppbv) from Summa Sampling.
-------
4594400
4594350
4594300
4594250
33
O
CO
CD
4593900
4593850
4593800
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
Figure 11.1,4-Dichlorobenzene Concentration Isopleths (ppbv) from Summa Sampling.
-------
INJ
4594400
4594350
4594300
4594250
4594200
4594150
459410
4594050
4594000
4593950
4593900
4593850
4593800
' / r >' -
./ t.f tf 1
•
C*'
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
O
09
Figure 12. Toluene Concentration Isopleths (ppbv) from Summa Sampling.
-------
CVS
on
4594400
4594350
4594300
4594250
4594200
4594150
4594100
4594050
4594000
4593950
4593900
4593850
4593800
3J
o
(A
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
Figure 13. Trichloroethene Concentration Isopleths (ppbv) from Summa Sampling.
-------
INJ
O5
4594400
4594350
4594300
4594250
4594200
4594150
4594100
4594050
4594000
4593950
4593900
4593850
4593800
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
O
09
Figure 14. Vinyl Chloride Concentration Isopleths (ppbv) from Summa Sampling.
-------
4594400
4594350
4594300
4594250
4594200
4594150
459410
4594050
4594000
4593950
4593900
4593850
4593800
33
O
CO
CD
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
Figure 15. m,p-Xylene Concentration Isopleths (ppbv) from Summa Sampling.
-------
INJ
oo
4594400
4594350
4594300
4594250
4594200
4594150
4594101
45940
4594000
4593950
4593900
4593850
4593800
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
O
09
Figure 16. o-Xylene Concentration Isopleths (ppbv) from Summa Sampling.
-------
CVS
CO
4594400
4594350
4594300
4594250
4594200
4594150
459410
4594050
4594000
4593950
4593900
4593850 f
4593800 •
33
O
CO
CD
291200 291250 291300 291350 291400 291450 291500 291550 291600 291650 291700 291750 291800 291850 291900 291950 292000
Figure 17. Rose Hill's Two Homogenous Parcels
-------
A Case Study
Table 3. Analytical Results for COPCs.
OJ
«
"S3
p
J3
CYifl ^
Paral <° & & ™i $ 8 g |
*=S - G
^ -H J3
Z -T PQ
(ppmvC) (ppmv) (ppnw)
137 0.19 1.2 56 42 3300 NDa 1.40
E 148 4.1 67 7.8 21 3600 ND 0.19
| 139 ND 0.31 56 43 2400 ND 1.80
2 140 1.8 44 23 31 2200 ND 0.14
131 ND 5.2 53 43 5100 0.58 0.58
c ISA 1.6 79 ND 21 560 ND ND
| 9 0.97 66 11 24 1100 ND 0.17
§ 16 ND 1.4 63 38 2700 ND 0.094
co
80 0.38 19 43 38 2200 ND 0.26
a ND = not detected
Table 4. COPCs 90th Percentile Concentrations for
Northern and Southern Parcels.
90th Percentile Concentration
(ppmv)
COPC Northern Parcel Southern Parcel
NMOC 4500 2550
1,1,1-TricliLoroethane 0.58
1,4-Dichlorobenzene 0.1008 0.1864
Benzene 1.64 0.242
CliLorobenzene 0.222 0.719
Cliloroethane 2.96 0.3202
Toluene 1.118 2.5473
Tricliloroelhene 0.0625 0.02741
Vinyl Chloride 0.62 0.2992
m,p-Xylene 6.73 3.75
o-Xylene 1.1 1.542
5,1 LandGEIVl Modeling of LFG
•*ji
With the 90th percentile values derived from the data set,
these data were then used as input values for the LandGEM
model to estimate the LFG emission rates for each of the
COPCs. Because there are two distinct parcels, it was nec-
essary to break this site into two areas and model each
individually for NMOC emissions. To model this site the
following parameters were used:
1 Methane generation rate (k): 0.05/yr [AP-42 default]
2 Methane generation potential (Zo): 170 m3/Mg [AP-
42 default]
TlT
1 Chlorobenzene
0.23
0.04
0.19
ND
ND
ND
0.62
0.73
ND
3
4
5
6
7
8
OJ
OJ
N
g go;
£ •§ % ^
S t- -S ;= oj
jS o "53 ,° G
•5 "73 o jj« 1>s G
0 •" G -2 & £
1 3 1 1 f | *
o - r £ £ > g 6
(ppmv) (ppmv) (ppmv) (ppmv) (ppmv) (ppmv) (ppmv)
0.47 0.06 0.06 ND ND 7.90 0.46
4.00 ND ND ND 0.80 ND 0.09
0.87 0.03 1.40 0.07 0.12 3.50 1.10
0.09 0.03 0.07 ND 0.20 0.50 0.30
1.40 0.12 0.46 0.02 0.17 4.00 1.10
0.041 0.026 0.091 0.0041 ND 0.0042 ND
0.021 0.038 0.019 ND 0.022 0.63 0.11
ND 0.25 0.018 ND ND 1.3 0.051
0.39 0.034 3.6 0.03 0.33 4.8 1.9
Year Opened: 1967
Current Year: 2003
Landfill Type: Co-disposal
Landfill Capacity: 197,692 Mg
This value was derived using the refuse estimator
within LandGEM. In order to derive this value, the
size of both parcels was estimated to be approximately
half of the total acreage of the solid waste landfill.
Therefore, each parcel was estimated to be 14 acres.
In addition, it was determined from a literature review
of the site that each parcel was approximately 18 feet
deep. With this information, LandGEM calculated the
appropriate landfill capacity.
Acceptance rate (1967-1981): 13,179.48 Mg/yr
This value was calculated using the Autocalc function
within LandGEM. This was performed due to a lack
of historical acceptance rate data available for this site.
To perform this calculation the landfill capacity value
just calculated was entered as the refuse in place for
the year 1982, as historical data indicated this was the
year the site was closed and maximum capacity was
achieved. Once the refuse in place was entered for the
year 1982, all years in which the landfill was active
were selected, including closure year (1967-1982).
With these years selected, the Autocalc function was
initiated, and the acceptance rate was derived for each
of the active years as an average value for all years
selected.
Methane percentage: 56% (Northern), 59% (Southern)
This was based on the 90th percentile of the field
sample data results.
30
-------
Rose Hill, Rl
9 NMOC Concentration: 4500 ppmv (Northern), 2550
ppmv (Southern)
This was based on the 90th percentile of the field
sample data results.
10 Air Pollutants (COPCs)
Modified per 90th percentile values as shown in Table
4.
With all values input for each parcel, LFG emission rates
for each COPC were estimated using the LandGEM model.
Table 5 provides the emission rates estimated for each
COPC within each landfill parcel, and Appendix D con-
tains all the LandGEM model runs for both parcels. Figure
18 shows the emission rate data for NMOCs over a 236
year time span, and Figure 19 shows an example output
file for NMOC emissions from the LandGEM model.
the LandGEM model could, in turn, be multiplied by this
unity-derived concentration to determine the 1-hour maxi-
mum concentrations for each COPC. To convert these con-
centrations to a representative annual concentration, all
derived 1-h concentrations were multiplied by the appro-
priate multiplying factor of 0.08 as identified in the guid-
ance report (EPA-600/R-05/123a). If an alternative aver-
aging time span is to be evaluated, the reader is referred to
section 2.2.1.4 - Dispersion Modeling and Table 2-3 of
the guidance report. Table 6 provides the maximum an-
nual concentrations for each COPC, and Appendix E con-
tains the SCREENS model runs for both parcels.
Table 5. Emission Rates of COPCs by Parcel.
2002 Emission Rate
5.2 Modeling of LFG
The next step in characterizing the emissions of LFG is to
.T O
evaluate the ambient impact of each of the COPCs. For
this, it is necessary to use an atmospheric dispersion model.
For demonstration purposes, SCREENS was used to pro-
vide a screening level assessment, and each parcel was
evaluated separately in order to properly screen the land-
fill. The landfill was broken into two rectangular parcels
as shown in Figure 17, and each parcel was treated as an
area source within the model. Each parcel was modeled at
a unity emission rate of 1 g/s to provide maximum 1-h
concentration for each parcel. Because each area was mod-
eled on a unity basis, the emission rates generated from
40
35 -
30 •
1 „„
i. 25 '
01
S
& 20 -
C
O
10 IP
I
Ul
10 -
E -
n -
ft
A
/ \
/ \
! \
,' \
« \
i i,
1 \
i \
1 \
I ^
1 \
,'
I \
\N
-' "\.
•*--.._
COPC
NMOC
1,1,1-Trichloroethane
1 ,4-Dichlorobenzene
Benzene
Chlorobenzene
Chloroethane
Toluene
Tricliloroethene
Vinyl Cliloride
m,p-Xylene
o-Xylene
(Mg/yr)
Northern Parcel Southern Parcel
12.84
2.562x10-3
4.868x10-"
4.243xl03
8.200x10-"
6.324x10-3
3.417x10-3
2.610x10-"
1.283x10-3
2.366xlO-2
3.867x10-3
6.907
8.779x10-"
5.893x10-"
2.547x10-3
6.489x10-"
7.385x10-3
1.239x10"
5.893x10-"
1.251x10-2
5.139x10-3
1965 1985 2005 2025 2045 2065 2085 2105 2125 2145 2165 2185 2205
Time (yr)
Figure 18. NMOC Emission Rates: 1967-2203
31
-------
A Case Study
Model Parameters
Lo : 170.00 mA3 / Mg ***** User Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 4500.00 ppmv ***** User Mode Selection *****
Methane : 56.0000 % volume
Carbon Dioxide : 44.0000 % volume
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year : 2003 Closure Year: 1982
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year : 13179.47 Mg/year
Model Results
NMOC Emission Rate
Year Refuse In Place (Mg) (Mg/yr) (Cubic m/
yr)
1968 1.318E+04 3.227E+00 9.002E+02
1969 2.636E+04 6.296E+00 1.757E+03
1970 3.954E+04 9.216E+00 2.571E+03
1971 5.272E+04 1.199E+01 3.346E+03
1972 6.590E+04 1.463E+01 4.083E+03
1973 7.908E+04 1.715E+01 4.784E+03
1974 9.226E+04 1.954E+01 5.451E+03
1975 1.054E+05 2.181E+01 6.085E+03
1976 1.186E+05 2.398E+01 6.689E+03
1977 1.318E+05 2.603E+01 7.263E+03
1978 1.450E+05 2.799E+01 7.809E+03
1979 1.582E+05 2.985E+01 8.328E+03
1980 1.713E+05 3.162E+01 8.822E+03
1981 1.845E+05 3.331E+01 9.292E+03
1982 1.977E+05 3.491E+01 9.739E+03
1983 1.977E+05 3.321E+01 9.264E+03
2001 1.977E+05 1.350E+01 3.766E+03
2002 1.977E+05 1.284E+01 3.583E+03
2003 1.977E+05 1.222E+01 3.408E+03
2201 1.977E+05 6.129E-04 1.710E-01
2202 1.977E+05 5.830E-04 1.627E-01
2203 1.977E+05 5.546E-04 1.547E-01
Table 6. Modeled Maximum Annual Concentrations.
Maximum Annual Concentrations
(Hg/m3)
COPC Northern Southern Total
NMOC 80.88 38.4 119.3
1,1,1-Trichloroethane 1.614xlO-2 0.00 1.614xlO-2
1,4-Dichlorobenzene 3.066xK)-3 4.88x10 3 7.946x10 3
Benzene 2.673xK)-2 3.28xlO-3 S.OOOxlO2
Chlorobenzene 5.165xK)-3 1.42xlO-2 1.932xlO-2
Chloroethane 3.983xK)-2 3.61xlO-3 4.344xU)-2
Toluene 2.152xK)-2 4.10xl02 6.257xl02
Trichloroethene 1.644xlQ-3 6.89x10-" 2.333xl03
Vinyl Chloride 8.081xK)-3 3.28xlQ-3 1.136xlO-2
m,p-Xylerie 1.490x10-' 6.95xlO-2 2.186x10-'
o-Xylene 2.436xl02 2.86xlO-2 5.292xlQ-2
Figure 19. Example LandGEM Model Run Output
32
-------
Rose Hill, Rl
Section 6. Risk Assessment
The risk assessment provided in this section is for illustra-
tive purposes only. It is not intended to represent a com-
plete and detailed risk assessment for determining further
actions at this site.
In order to calculate the incremental risk associated with
exposure to a COPC, the time averaged emission rate for
the time period of concern must first be determined. The
equation for determining the time averaged emission rate
is
< E>
(I/ED)
+E
where
< E > = Time-averaged emission rate (megagrams
per year),
ED = Exposure duration (years),
h = Time-step interval (years), h = 1 yr,
£0,1,2...» = Emission rate at the end of the first year
(E0) and each succeeding year from
LandGEM (megagrams per year), and
n = Number of time-steps (n = ED).
This time averaged emission rate is then entered into the
atmospheric dispersion model to estimate the average ex-
posure point concentration of the COPC. Using this ap-
proach, a dispersion model run will be required for each
chemical of concern. Alternatively, if the dispersion model
is run assuming the emission rate is at unity (1 g/m2»s), the
dispersion model will generate a normalized air concen-
tration in (micrograms per cubic meter per gram per square
meter second) at the receptor of concern. The estimated
ambient air concentration (micrograms per cubic meter) is
determined by multiplying the dispersion coefficient and
the time averaged emission rate. The LandGEM model runs
for the Somersworth Landfill predicted very low emission
rates, and the emission rate for every COPC was declining
from 2002 forward. Hence, it was decided to use only the
2002 emission rates to calculate, for illustrative purposes,
the ambient air concentrations. These predicted ambient
air concentrations were then compared to the target con-
centrations in Table 7.
Table 7. Risk Analysis
CAS
No.
75354
106467
71432
108907
75003
108883
79016
75014
108383
95476
Chemical
1 , 1 -Dichloroethylene
1 ,4-Dichlorobenzene
Benzene
Chlorobenzene
Chloroethane (ethyl chloride)
Toluene
Tricliloroethylene
Vinyl Chloride (chloroethene)
m,p-Xylene
o-Xylene
Basis
of
Target
Cone.
NCa
NC
Cb
NC
NC
NC
C
C
NC
NC
Qargot — Target Ambient Air Concentration to
Satisfy bodi
and the
R=1(H, HI=1
(jlg/m3)
2.2xlO+03
8.0x1 O*02
31.
60.
1.0x10°"
4.0xlO+02
2.2
28.
7.0xlO^°3
7.0xlO+"3
die Prescribed Risk Level (R)
Target Hazard Index (HI)
R=10 5, HI=1 R=10 6, HI=1
(fig/m3) Oag/m3)
2.2xlO+03 2.2xlO+"3
s.oxio*02 s.oxnr2
3.1 3.1x10-°'
60. 60.
l.OxlO^04 l.OxlO^04
4.0xlO-°2 4.0xlO-°2
0.22 2.2xlO-°2
2.8 0.28
7.0xlO+"3 7.0xlO-"3
7.0xlO+"3 7.0xlO+"3
Total
Ambient Air
Cone.
(^lg/m3)
1.6xlO-°2
7.9xlO-"3
3.0xl0^2
1.9xlO-°2
4.3xlO-°2
6.3xl0^2
2.3xl0^3
l.lxlO-02
2.2x10-°'
5.3xlO-°2
' NC = noncancer risk
' C = cancer risk
33
-------
A Case Study
Table 7 identifies target media concentrations correspond-
ing to risk or hazard based concentrations for ambient air
in residential settings. Only air concentrations that satisfy
both the prescribed cancer risk level and the target hazard
index are included in Table 7. The approach described here
also can be used to evaluate chemicals not listed in the
tables. It must be emphasized that the concentrations pre-
sented in Table 7 are screening levels. They are not clean-
up levels or preliminary remediation goals nor are they
intended to supercede existing criteria of the lead regula-
tory authority. The lead regulatory authority for a site may
determine that criteria other than those provided herein are
appropriate for their specific site or area.
The sources of chemical data used in the calculations nec-
essary to create Table 7 were EPA's Superfund Chemical
Data Matrix (SCDM) database and EPA's Water 9 data-
base whenever a chemical was not included in the SCDM
database. EPA's Integrated Risk Information System (IRIS)
is the preferred source of carcinogenic unit risks and non-
carcinogenic reference concentrations (RfCs) for inhala-
tion exposure.' The following two sources were consulted,
in order of preference, when IRIS values were not avail-
able: provisional toxicity values recommended by EPA's
National Center for Environmental Assessment (NCEA)
and EPA's Health Effects Assessment Summary Tables
(HEAST). If no inhalation toxicity data could be obtained
from IRIS, NCEA, or HEAST, extrapolated unit risks and
RfCs were derived by using toxicity data for oral exposure
(cancer slope factors and reference doses, respectively)
from these reference sources using the same preference
order. Toxicity databases such as IRIS are constantly be-
ing updated; this table is current as of August 2002. Users
of this guidance are strongly encouraged to research the
latest toxicity values for contaminants of interest from the
sources noted above.
The ambient air concentrations in the table are risk-based
screening levels calculated following an approach consis-
tent with that presented in HEAST (U.S. EPA, 1997). Sepa-
rate carcinogenic and non-carcinogenic target concentra-
tions were calculated for each compound when both unit
risks and reference concentrations were available. When
inhalation toxicity values were not available, unit risks and
reference concentrations were extrapolated from oral slope
factors or reference doses, respectively. For both carcino-
gens and non-carcinogens, target air concentrations were
1 U.S. EPA. 2002. Integrated Risk Information System (IRIS).
http://www.epa.gov/iriswebp/irls/index.html (accessed October
2005)
based on an adult exposure scenario and assume maximum
exposure of an individual (i.e., exposure to contaminants
24 hours per day, 7 days per week, over 30-year residen-
tial exposure). An inhalation rate of 20 mVday and a body
weight of 70 kg are assumed and have been factored into
the inhalation unit risk and reference concentration toxic-
ity values.
Unit risks were extrapolated from cancer slope factors us-
ing
1 VlO'"
URF = CFS x IR x
where
URF = unit risk factor (micrograms per cubic
meter)"1,
CSF = cancer slope factor,
IR = inhalation rate (cubic meters per day), and
BW = body weight (kilograms).
Reference concentrations were extrapolated from reference
doses using
1
where
RfC = RfDx BWx —
. IR
R/C = reference concentration (milligram per
cubic meter) and
RfD = reference dose (milligram per kilogram per
day).
For carcinogens,
Ccancer = TCR/URF
and for noncarcinogens,
where
CcM1cer = target indoor air carcinogen concentration
(micrograms per cubic meter),
Cnaneancer = target indoor air noncarcinogen concen-
tration (micrograms per cubic meter),
TCR = target cancer risk (e.g., 1.0x10 5), and
THO = target hazard quotent (e.g., 1.0).
For most compounds, the more stringent of the cancer- and
non- cancer-based contaminant concentrations is chosen as
the target air concentration that satisfies both the prescribed
cancer risk level and the target hazard quotient.
34
-------
Rose Hill, Rl
^target.ia ~ Mil V((_xcancer, tsnon-canceff
The target concentration, however, was preferentially se-
lected for those compounds that had both an inhalation-
based toxicity value and an oral-extrapolated value. The
selected screening level was preferentially based on the
non-extrapolated toxicity value chosen to calculate the ac-
ceptable ambient air concentration.2
For ease in application of the table, the indoor air concen-
trations are given in units of micrograms per cubic meter.
The conversion from parts per billion by volume to micro-
grams per cubic meter is
= C
n?
*10!
aim
in
1
where
R= gas constant (0.0821 L»atm/mole»K),
T= absolute temperature (298 K), and
MW= molecular weight (grams per mole).
The calculated target air concentrations are listed in the
tables along with a column indicating whether cancer or
noncancer risks drive the target concentration. If the expo-
sure scenario of concern is an adult resident living at the
receptor location being most impacted, the forward-calcu-
lation of incremental risks begins with the estimated ambi-
ent air concentration (i.e., Cair in micrograms per cubic
meter). For carcinogenic contaminants, the risk level is
calculated as
URFx
where
ATC x 365days/yr
Risk= incremental risk level, unitless (e.g.,
1x106),
2 The target air concentration for trichloroethylene is the lone
exception to this rule. The target concentration is based on a
carcinogenic unit risk extrapolated from an upper bound oral
cancer slope factor of 4x1 CH (mg/kg/day)"1 cited in NCEA's draft
risk assessment for trichloroethylene (EPA, 2001). However, as
noted in that document, available evidence from toxicological
studies suggests similar carcinogenic effects from both the oral
and inhalation routes of exposure. The existence of this evidence
gives greater weight to the extrapolated unit risk, and given that
the unit risk produces a lower target concentration than the non-
extrapolated RfC, the unit risk-based value is adopted here as
the target air concentration for trichloroethylene.
Cgjr = annual average ambient air concentration
for each carciogen (micrograms per cubic
meter),
ATC = averaging time for carcinogens (years—70
yr),
EF= exposure frequency (days per year—350
days), and
ED = exposure duration (years—30 yr).
For noncarcinogenic contaminants, the hazard quotient is
calculated as
EFx ED>
HQ--
ATNC x 365 days/yr
where
HQ= Hazard quotient, unitless (e.g., 1.0) and
ATNC= Averaging time for noncarcinogens
(year—30 yr)
Table 7 illustrates the results of using the above equations
and discussions. The last column in Table 7 represents the
total ambient air concentration in micrograms per cubic
meter. This value is derived by multiplying the emission
flux values from LandGEM by the ambient air concentra-
tion from the dispersion model (SCREENS) when run at a
unity emission rate (1 g/s). These values would be com-
pared to the appropriate risk derived concentrations as seen
in the previous three columns to determine if a particular
COPC is above or below an acceptable air concentration
and whether further actions or investigations may be
needed. For purposes of comparison, approximately 12
COPCs were identified in one or more of the ambient air
samples that were collected approximately 3 ft above
ground level and adjacent to the subsurface probes. The
maximum concentration was always below 20 ppbv (0.3
|ig/m3) Again Table 7 is presented for illustrative purposes
only and is not intended to represent the results or conclu-
sions drawn from a detailed risk assessment.
35
-------
A Case Study
36
-------
Rose Hill, Rl
Section 7. Findings and Conclusions
This case study documents how the guidance can be used
to evaluate landfill gas emissions. It illustrates the useful-
ness of both the information and the procedures presented
in the Guidance for Evaluating Landfill Gas Emissions from
Closed or Abandoned Facilities. By applying the investi-
gative techniques and recommended practices, the research
team was able to:
1 Determine where the landfill gases are escaping into
the atmosphere,
2 Identify the chemicals of potential concern,
3 Quantify the speciated LFG emission rates ,
4 Identify the most likely to be affected at off-site
location (s), and
5 Characterize ambient air concentrations.
This case study report provided data and information that
were used by the remedial project manager to:
1 Assess the health risk associated with the emissions
from the landfill,
2 Determine if additional site investigation effort is
needed,
3 Evaluate the level of effort associated with the exist-
ing LFG monitoring program,
4 Determine if the previously proposed remedial design
needed to be altered,
5 Evaluate the need for institution controls and future
land use policy decisions, and
6 Decide if the risks and hazards associated with the land-
fill gas needed to be controlled with LFG control tech-
nology.
Specific to the Rose Hill site the following lessons were
learned:
• The conventional field screening, discrete sampling
using Summa canisters, commercial laboratory analy-
sis using TO 15 analytical methods, and emission and
dispersion modeling procedures provided the informa-
tion needed to assess the risks and hazards associated
with LFG emissions. The turn-around time for the com-
mercial laboratory was measured in weeks. The data
reduction and modeling efforts require 2-3 man days
of effort. Hence, health risks could not be quantified
on a real time basis. Readily available equipment and
ordinary environmental technician skills are required
to obtain quality results.
• The conventional field screening, discrete sampling
using Tedlar bags, onsite mobile laboratory using EPA
Modified Method 18 analytical procedures, and emis-
sion and dispersion modeling procedures provided the
information needed to assess the risks and hazards as-
sociated with LFG emissions. The onsite mobile labo-
ratory was unable to quantify the toxic COPCs con-
centrations because of detection limit issues.
• Using the research data, the predicted COPC ambient
air concentrations are below that which would create
an unacceptable risk at the lxlO~6 level.
37
-------
A Case Study
-------
Rose Hill, Rl
Appendix A
Site Activity Photographs
A-l
-------
A Case Study
Rose Hill Superfund Landfill
Old Maintenance Shed on Landfill Property
A-2
-------
Rose Hill, Rl
Access Road onto Landfill Property
a-'ft
Storm Drain on Landfill Property
A-3
-------
A Case Study
Rosehill Site Terrain
Overgrowth on the Rose Hill Site
A-4
-------
Rose Hill, Rl
Passive Vent at Grid 80
-• w.x-ni..A u-:
Passive Vent at Grid 131
A-5
-------
A Case Study
Passive Vent at Grid 140
Sampling Crew Navigating into Thick Overgrowth
A-6
-------
Rose Hill, Rl
Rose Hill Recycling-Transfer Station
Serving Smith Kingstown and Narragansctt
OPERATING HOURS
MONDAY-SATURDAY 7:00am - 3:00pm
CLOSED Sundays and Holidays
NO LIQUtO CHEMICALS. SEPTIC OB HAZARDOUS WASTE
(ill HUH M .1: I-MIII-I |.| \M»I tur inlninuiutn an i»v,il nl tli»r Htm
Rose Hill Transfer Station East of the Landfill
Entrance to the Rose Hill Transfer Station and its Ptoximity to the Landfill
A-7
-------
A Case Study
Newly Paved Public Road South of the Landfill
ERTC TAGA Unit Parked Along the Western Property Boundary
A-8
-------
Rose Hill, Rl
Sampling Crew Staging for Sample Collection Activities
Slam-Bar Used for Sampling Probe Insertion
A-9
-------
A Case Study
Fixed Gas Sampling Collected by Sampling Probe
Tedlar Bag Chamber and Summa Canister Sampling
A-10
-------
Rose Hill, Rl
QA/QC Sampling with Summa Canisters
Tedlar Bag and Summa Canister Ambient Air Sampling
A-ll
-------
A Case Study
Passive Vent Gas Sampling
Perimeter Well Sampling
A-12
-------
Rose Hill, Rl
Appendix B
Wilcoxon Statistical Analysis
B-l
-------
A Case Study
Wilcoxon Two-Sample, Rank-Sum Test
In order to properly characterize and establish a sampling
method for each landfill, it is necessary to identify those
areas that are nearly homogeneous in composition. This is
determined following the screening procedures. Through
application of statistical methods on the screening data, it
is possible to divide the landfill into nearly homogeneous
areas. For the purpose of this guidance, it was decided to
use a method referred to as the Wilcoxon two-sample, rank-
sum test, or simply the rank-sum test. This is a statistical
method used to determine if two independent sample popu-
lations are statistically similar (i.e., they have the same mean
and median). For this application, statistically similar popu-
lations refer to areas within the landfill that are nearly ho-
mogeneous.
The first step is to assign the screening data that was col-
lected to two populations (e.g., north landfill and south
landfill) as
n = n
n2
where
n = entire screening data set,
Ik = population of size nl:
n2 = population of size n2, and
A Zai2, then the two popu-
lations can not be considered statistically similar and are
therefore two nonhomogeneous areas.
Continue this process until all areas of the landfill have
been divided into distinct homogeneous areas.
B-2
-------
Rose Hill, Rl
TABLE X DISTRIBUTION OF THE RANK SUM T
The values of T'a. 7"',_a. and a are such that, if the n} and n3 observations are
chosen at random from the same population, the chance that the rank sum
T' of the nt observations in the smaller sample is equal to or less than T'a is
a and the chance that 7"'is equal to or greater than T\ a is a. The sample
sizes are shown in parentheses (nl, r>2)
T. T',., „
(1.9)
1 10 .100
(1.10)
1 11 091
(2,3)
3 9 100
(2.4)
3 11 .067
(2.5)
3 13 .047
4 12 .095
(2,6)
3 15 .036
4 14 .071
(2.7)
3 1 7 .028
4 16 .056
(2.8)
3 19 .022
4 18 .044
5 1 7 .089
(2,9)
3 21 .018
4 20 .036
5 19 .073
(2.10)
3 23 .015
4 22 .030
5 21 .061
6 20 .091
(3,3)
6 15 .050
7 14 .100
(3,4)
6 18 .028
7 17 057
(3.5)
6 21 018
7 20 .036
8 19 071
(3.6)
6 24 .012
7 23 .024
8 22 .048
9 21 .083
(3,7)
6 27 .008
7 26 .017
8 25 .033
9 24 .058
10 23 .092
n r;.. <•
(3,8)
6 30 .006
7 29 .012"
8 28 .024
9 27 .042
10 26 .067
11 25 .097
(3,9)
6 33 .005
7 32 .009
8 31 .018
9 30 .032
10 29 .050
11 28 073
(3,10)
6 36 .003
7 35 .007
8 34 .014
9 33 .024
10 32 .038
11 31 .056
1 2 30 .080
(4.4)
10 26 .014
11 25 .029
12 24 057
13 23 .100
(4.5)
10 30 .008
11 29 .016
12 28 .032
13 27 .056
14 26 .095
(4,6)
10 34 .005
11 33 .010
12 32 .019
13 31 .033
14 30 .057
15 29 .086
(4.7)
10 38 .003
1 1 37 .006
12 36 .012
13 35 .021
14 34 .036
15 33 .055
16 32 .082
(4.8)
10 42 .002
11 41 .004
r. T\-. o
(4,8) {Com )
12 40 008
13 39 014
14 38 024
15 37 .036
16 36 055
17 35 .077
(4.9)
10 46 001
1 1 45 .003
12 44 006
13 43 .010
14 42 .017
15 41 .025
16 40 .038
17 39 053
18 38 .074
19 37 .099
(4,10)
10 50 .001
1 1 49 .002
1 2 48 004
13 47 .007
14 46 .012
15 45 .018
16 44 .026
17 43 .038
18 42 .053
19 41 .071
20 40 094
(5,5)
15 40 .004
16 39 .008
17 38 .016
18 37 .028
19 36 .048
20 35 .075
(5.6)
15 45 .002
16 44 .004
17 43 .009
18 42 .015
19 41 .026
20 40 .041
21 39 .063
22 38 .089
(5.7)
15 50 .001
16 49 .003
1 7 48 .005
18 47 .009
T'. r,.. a
(5.7) (Com .)
19 46 .015
20 45 .024
21 44 .037
22 43 .053
23 42 .074
(5.8)
15 55 .001
16 54 .002
1 7 53 .003
18 52 .005
19 51 .009
20 50 .015
21 49 023
22 48 .033
23 47 .047
24 46 .064
25 45 .085
(5,9)
1 5 60 .000
16 59 .001
1 7 58 .002
18 57 .003
19 56 .006
20 55 .009
21 54 .014
22 53 .021
23 52 .030
24 51 .041
25 50 .056
26 49 .073
27 48 .095
(5,10)
15 65 .000
16 64 .001
17 63 .001
18 62 .002
19 61 .004
20 60 .006
21 59 .010
22 58 .014
23 57 .020
24 56 .028
25 55 lOSS
26 54 .050
27 53 .065
28 52 .082
(6.6)
21 57 .001
22 56 .002
23 55 .004
B-3
-------
A Case Study
DISTRIBUTION OF THE RANK SUM T (continued)
r. r,_ 0
(6,6) (Com )
24 54 .008
25 53 .013
26 52 .021
27 51 032
28 50 .047
29 49 .066
30 48 .090
(6.7)
21 63 .001
22 62 .001
23 61 .002
24 60 .004
25 59 .007
26 58 .011
27 57 .017
28 56 .026
29 55 .037
30 54 .051
31 53 .069
32 52 .090
(6.8)
21 69 .000
22 68 .001
23 67 .001
24 66 .002
25 65 .004
26 64 .006
27 63 .010
28 62 .015
29 61 .021
30 60 .030
31 59 .041
32 58 .054
33 57 .071
34 56 .091
(6.9)
21 75 .000
22 74 .000
23 73 .001
24 72 .001
25 71 .002
26 70 .004
27 69 .006
28 68 .009
29 67 .013
30 66 .018
31 65 .025
32 64 .033
33 63 .044
34 62 .057
r. TJ-. «
(6,9) (ConTT)
35 61 .072
36 60 .091
(6.10)
21 81 .000
22 80 .000
23 79 .000
24 78 .001
25 77 .001
26 76 .002
27 75 .004
28 74 .005
29 73 .008
30 72 .011
31 71 .016
32 70 .021
33 69 .028
34 68 .036
35 67 .047
36 66 .059
37 65 .074
38 64 .090
(7.7)
28 77 .000
29 76 001
30 75 .001
31 74 .002
32 73 .003
33 72 .006
34 71 .009
35 70 .013
36 69 .019
37 68 .027
38 67 .036
39 66 .049
40 65 .064
41 64 .082
(7,8)
28 84 .000
29 83 .000
30 82 .001
31 81 .001
32 80 .002
33 79 .003
34 78 .005
35 77 .007
36 76 .010
37 75 .014
38 74 .020
39 73 .027
40 72 .036
r. *;_ „
(7.8) (Cont.)
41 71 .047
42 70 060
43 69 .076
44 68 .095
45 67 116
(7.9)
28 91 .000
29 90 .000
30 89 .000
31 88 .001
32 87 .001
33 86 .002
34 85 .003
35 84 .004
36 83 .006
37 82 .008
38 81 .011
39 80 .016
40 79 .021
41 78 .027
42 77 .036
43 76 .045
44 75 .057
45 74 .071
46 73 .087
(7,10)
28 98 .000
29 97 .000-
30 96 .000
31 95 .000
32 94 .001
33 93 .001
34 92 .001
35 91 .002
36 90 .003
37 89 .005
38 88 .007
39 87 .009
40 86 .012
41 85 .017
42 84 .022
43 83 .028
44 82 .035
45 81 .044
46 80 .054
47 79 .067
48 78 .081
49 77 .097
(8,8)
36 100 .000
r. 7U .
(8,8) (Cont.)
37 99 000
38 98 .000
39 97 .001
40 96 .001
41 95 .001
42 94 .002
43 93 .003
44 92 .005
45 91 .007
46 90 .010
47 89 .014
48 88 .019
49 87 .025
50 86 .032
51 85 .041
52 84 .052
53 83 .065
54 82 .080
55 81 .097
(8.9)
36 108 .000
40 1 04 000
41 103 .001
42 102 .001
43 101 .002
44 100 .003
45 99 .004
46 98 .006
47 97 .008
48 96 .010
49 95 .014
50 94 .018
51 93 .023
52 92 .030
53 91 .037
54 90 .046
55 89 .057
56 88 .069
57 87 .084
(8,10)
36 116 .000
41 111 .000
42 110 .001
43 109 .001
44 108 .002
45 107 .002
46 106 .003
47 105 .004
48 104 .006
49 103 .008
B-4
-------
Rose Hill, Rl
DISTRIBUTION OF THE RANK SUM P (continued)
T, T',-, «
(8.10) (Cont.)
50 102 .010
51 101 .013
52 100 .017
53 99 022
54 98 .027
55 97 .034
56 96 .042
57 95 .051
58 94 .061
59 93 .073
60 92 .086
(9.9)
45 126 .000
50 121 .000
51 120 .001
52 119 001
53 118 .001
54 117 .002
55 116 003
56 115 .004
57 114 .005
r. r,_. a
(9.9) (Cont.)
58 113 .007
59 112 .009
60 111 .012
61 110 .016
62 109 .020
63 108 .025
64 107 .031
65 106 .039
66 105 .047
67 104 .057
68 103 068
69 102 .081
70 101 .095
(9.10)
45 135 .000
52 128 000
53 127 .001
54 126 .001
55 125 .001
56 124 .002
57 123 .003
r. r,_ 0
(9,10) (Com.)
58 122 .004
59 121 .005
60 120 .007
61 119 .009
62 118 .011
63 117 .014
64 116 .017
65 115 .022
66 114 .027
67 113 .033
68 112 .039
69 111 .047
70 110 .056
71 109 .067
72 108 .078
73 107 .091
(10.10)
65 145 .001
66 144 .001
67 143 .001
68 142 .002
f. r,_. a
(10,10) (Cont.)
69 141 .003
70 140 .003
71 139 .004
72 138 .006
73 137 .007
74 136 .009
75 135 .012
76 134 .014
77 133 .018
78 J32 .022
79 131 .026
80 130 .032
81 129 .038
82 128 .045
83 127 .053
84 126 .062
85 125 .072
86 124 .083
87 123 .095
B-5
-------
A Case Study
TABLE IV I DISTRIBUTION
df
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
inf.
.100
3.078
1.886
1.638
1.533
1.476
1.440
1.415
1.397
1.383
1.372
1.363
1.356
1.350
1.345
1.341
1.337
1.333
1.330
1.328
1.325
1.323
1.321
1.319
1.318
1.316
1.315
1.314
1.313
1.311
1.282
.050
6.314
2.920
2.353
2.132
2.015
1.943
1.895
1.860
1.833
1.812
1.796
1.782
1.771
1.761
1.753
1.746
1.740
1.734
1.729
1.725
1.721
1.717
1.714
1.711
1.708
1.706
1.703
1 . 701
1.699
1.645
.025
12.706
4.303
3.182
2.776
2.571
2.447
2.365
2.306
2.262
2.228
2.201
2.179
2.160
2.145
2.131
2.120
2.110
2.101
2.093
2.086
2.080
2.074
2.069
2.064
2.060
2.056
2.052
2.048
2.045
1.960
.010
31.821
6.965
4.541
3.747
3.365
3.143
2.998
2.896
2.821
2.764
2.718
2.681
2.650
2.624
2.602
2.583
2.567
2.552
2.539
2.528
2.518
2.508
2.500
2.492
2.485
2.479
2.473
2.467
2.462
2.326
.005
63.657
9.925
5.841
4.604
4.032
3.707
3.499
3.355
3.250
3.169
3.106
3.055
3.012
2.977
2.947
2.921
2.898
2.878
2.861
2.845
2.831
2.819
2.807
2.797
2.787
2.779
2.771
2.763
2.756
2.576
df
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
inf.
B-6
-------
Rose Hill, Rl
Rose Hill Landfill Site
22-24 July 2002
Wilcoxon Rank Sum Analysis (Run 1)
Population 1 size (/?,)
Population 2 size (n2)
Total population size (ri)
Sum of Ranks (WQ
Large Sample Statistic
Confidence Interval
Z^
Accept or Reject H0?
11
14
25
209
3.683
5.0%
1.708
REJECT
Rose Hill Landfill Site
22-24 July 2002
Wilsoxon Rank Sum Analysis (Run 1)
Grid
No.
1
2
3
4
5
7
8
9
10
13
15
16
19
25
129
137
138
139
143
146
148
163
176
179
180
LJTM Coordinates
of Grid Node *
Easting
291624
291654
291684
291714
291744
291744
291744
291684
291654
291594
291654
291684
291774
291684
291684
291594
291624
291654
291774
291864
291834
291624
291684
291594
291564
Northing
4593806
4593806
4593806
4593806
4593806
4593836
4593836
4593836
4593836
4593866
4593866
4593866
4593866
4593896
4594196
4594226
4594226
4594226
4594226
4594226
4594256
4594286
4594316
4594316
4594316
IMOC NMOC. Assign p^ No. Ties ^ Pop. 1
Conc' Rank P°P- Set Ranki"S 15 Rankin§ ZOSM)
0.20
0.43
0.20
0.20
0.20
0.20
0.20
1.80
0.40
0.20a
0.30
0.60
0.26
0.20
0.25
2.50
0.50
5.00
2.00
2.00'1
2.00
1.00
2.00
1.00
1.00
0.2
0.43
0.2
0.2
0.2
0.2
0.2
1.8
0.4
0.2
0.3
0.6
0.26
0.2
0.25
2.5
0.5
5
2
2
2
1
2
1
1
2
2
2
2
2
2
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
13
1
1
1
1
1
19
12
1
11
15
10
1
9
24
14
25
20
20
20
16
20
16
16
8
1
8
8
8
8
8
1
1
8
1
1
1
8
1
1
1
1
4
4
4
3
4
3
3
4.5
13
4.5
4.5
4.5
4.5
4.5
19
12
4.5
11
15
10
4.5
9
24
14
25
21.5
21.5
21.5
17
21.5
17
17
9
24
14
25
21.5
21.5
21.5
17
21.5
17
17
a Duplicate value from grid 15 used.
b Duplicate value from g'od 148 used.
B-7
-------
45S4400
45S4200
W
oo
45S4000
45S3800
fr A,
\
.
11V
11C
\
V
I,
190
—
,
• * A A
• ^ *
1* • • • •<
I
I
Jk
I N1
-- N2
I
i
i
i
-i
+• Locations where NMOCs
were detected
291200
291400
291600
291800
292000
Rose Hill Screening Sampling Locations for Wilcoxon Run 1 Populations
o
09
V)
-------
Rose Hill, Rl
Rose Hill Landfill Site
22-24 July 2002
Wilcoxon Rank Sum Analysis (Run 2)
Population 1 size (n^ 3
Population 2 size (n2) 8
Total population size (n) 11
Sum of Ranks (WQ 22.5
Large Sample Statistic (Zrs) SEE TABLE X
Confidence Interval 5.0%
ZLO, SEE TABLE X
Accept or Reject H0? H0 ACCEPTED
Rose Hill Landfill Site
22-24 July 2002
Wilsoxon Rank Sum Analysis (Run 2)
UTM Coordinates ,,,,„„
9Pd of Grid Node NMOC
Assign Prelim No-Ties Final w
T~l»^-^. C*-» * Ti ™-»1,..J.~™ T~J ,™.«,1 ,..!.„„. «* rs
Easting Northing Rank
129
137
138
139
143
146
148
163
176
179
180
291684
291594
291624
291654
291774
291864
291834
291624
291684
291594
291564
4594196
4594226
4594226
4594226
4594226
4594226
4594256
4594286
4594316
4594316
4594316
0.25
2.50
0.50
5.00
2.00
2.00a
2.00
1.00
2.00
1.00
1.00
0.25
2.5
0.5
5
2
2
2
1
2
1
1
2
2
2
2
1
1
1
2
2
2
2
1
10
2
11
6
6
6
3
6
3
3
fj J.VU
1
1
1
1
4
4
4
3
4
3
3
"•"•"•& 22.5
1
10
2
11
7.5
7.5
7.5
4
7.5
4
4
7.5
7.5
7.5
Duplicate value from g'od 148 used.
B-9
-------
4594400
4594200
4594000
4593800
T.
1^
111 _
1C
\
\
I
N —
0 ^
* 190
—
__
• ^
|fe
—
,
_^X
I
I
I
I
I
I
1
-
•
1
+• Locations where NMOCs
were detected
291200
291400
291600
291800
292000
Rose Hill Screening Sampling Locations for Wilcoxon Run 2 Populations
O
09
V)
-------
Rose Hill, Rl
Rose Hill Landfill Site
22-24 July 2002
Wilcoxon Rank Sum Analysis (Run 3)
Population 1 size (A)
Population 2 size (n2)
Total population size (/?)
Sum of Ranks (Wr)
Large Sample Statistic
Confidence Interval
Zl-a
Accept or Reject H0?
5
9
14
42
SEE TABLE X
5.0%
SEE TABLE X
Hn ACCEPTED
Rose Hill Landfill Site
22-24 July 2002
Wilsoxon Rank Sum Analysis (Run 3)
Grid ]
No.
1
2
3
4
5
7
8
9
10
13
15
16
19
25
LJTM Coordinates A
of Grid Node *
Easting
291624
291654
291684
291714
291744
291744
291744
291684
291654
291594
291654
291684
291774
291684
Northing
4593806
4593806
4593806
4593806
4593806
4593836
4593836
4593836
4593836
4593866
4593866
4593866
4593866
4593896
IMOC N
Cone. j
0.20
0.43
0.20
0.20
0.20
0.20
0.20
1.80
0.40
0.20a
0.30
0.60
0.26
0.20
MOfC Assign Prelim No"
flank P°P- Set Ranking
0.2
0.43
0.2
0.2
0.2
0.2
0.2
1.8
0.4
0.2
0.3
0.6
0.26
0.2
1
1
2
2
2
2
2
2
1
1
1
2
2
2
1
12
1
1
1
1
1
14
11
1
10
13
19
1
Ties Final P°P- 1
8 Rankin§ 42.0
8
1
8
8
8
8
8
1
1
8
1
1
1
8
4.5
12
4.5
4.5
4.5
4.5
4.5
14
11
4.5
10
13
9
4.5
4.5
12
11
4.5
10
Duplicate value from grid 15 used.
B-ll
-------
45S4400
45S4200
45S4000
45S3800
fr A,
\
.
11V
11C
\
V
II
.-,
— _
— ,
• A
1«— •-
190
- —
• »-
& .*.
V
-• — • — «r
I
I
I
I
I
I
i
- N,
+• Locations where NMOCs
were detected
291200
291400
291600
291800
292000
Rose Hill Screening Sampling Locations for Wilcoxon Run 3 Populations
o
09
V)
-------
Rose Hill, Rl
Appendix C
Laboratory Results
C-l
-------
Table 1. Comparison of October 2002 Analysis Results of Rose Hill Volatile Organic Compounds in Air.
Sample Number
Sample Location
Dichlorodifluoromethane
Dichlorotetrafluoroethane
Vinyl Chloride
Chloroethane
Trichlorofluoromethane
Isopropyl Alcohol
Acetone
1,1-Dichloroethene
Methyiene Chloride
trans- 1 ,2-Dichloroethene
Hexane
1,1-Dichloroethane
2-Butanone
cis-1 ,2-Dichloroethene
1 ,1.1-Trichloroethane
Cyclohexane
Carbon Tetrachloride
1,2-Dichloroethane
Benzene
Heptane
Trichloroethene
1 ,2-Dichloropropane
Toluene
Tetrachloroethene
Chlorobenzene
Ethylbenzene
m&p-Xylenes
o-Xylene
Styrene
4-Ethyltoluene
1 ,3,5-Trimethylbenzene
1 ,2,4-TrlmethyIbenzene
1 ,3-Dichlorobenzene
1 ,4-Dichlorobenzene
1 ,2-Dichlorobenzene
13500
Grid 137
1500
120
U
770
U
U
U
U
U
9.1
2800
U
U
12
U
3000
U
U
2200
5200
U
U
99
U
330
5800
8600
430
150
950
450
1100
U
76
U
MM-JftW-.n.r,
<3rfd137
,,i,,,,1W9",,,,,,..
„,„•„„.?#„•„„„
, .„„«„„„„.„
mi,lll470MI,,,l,
„ , , V, ,„,-
,„„„ J4IlI11IlM1
, ....VL,
U
U
U
M,,,,,,^,, „,„
,„, ,,,,JU,,,,,,,M,
,„„„„„$„„•„•„,
„,¥,„,,
.,.,,,„.„«,.„ ,...
.......jwp, ,
,l,,l,MI,M,n, „,
U
,„ ,1*00,.,,.
4100
,„„,¥, •„„„
U
, , , , ,&,
U
.,„ ,230 ,..,....
.jjflw,,,,,,,,
7900, ,
-ni,,,,-4^,, ,,.
,,-m ^ ,-„•-,,
,rr,,$8,-,-n
, .$&,.„ ,.,..,
,,,,-,J200, ,.,„.
., ,.,V,,--,- •
,„„„„» ,
u
%
Diff.
6.7
0.0
39
7.1
47
35
21
41
30
6,9
8.1
7.0
17
2.2
9.1
26
13499
Grid 137 D.
1500
120
U
590
U
U
U
U
U
9.8
2800
U
U
13
U
3000
U
U
2200
5200
U
U
79
U
340
5800
8600
410
120
940
450
1100
U
74
U
12942 tnii
Gr'w'js^aiip^
tm, i
tllm :
„„„„«,,„,,„•
„, ffiL,,,,,,-
..nuHMuM,,, .,,,,:
....M,,,,,,-,,,,-
n,,,,,,,,,,,^,,.,,
,,,,,,-M.M,,.,,,,,....
MI1M ,,„:
U
im
.....M,,,,,,-,,,,-1
„ M,,..,,,
1M11M
M,.,. ,.
1^00
,.„„,., ^f
u
JW,,.,,,
Ml, 42pp ,„„
m,,M „ „
, ,u ,Ur , „„
6t> ,
.MMMM,,,,,,,,,,,,'
5909 ,
,l,.,.,,l?7.09,,,,,,
.,. .4»
u .
840
480
1200
,M,W--n,
64
U
%
Diff.
13
0.0
22
7.1
47
36
19
24
32
3.4
1.2
20
11
6.7
9.1
14
13498
Grid 137Amb.
U
U
U
U
U
U
15
U
U
U
8.2
U
U
U
u
u
u
u
7.1
17
U
U
4.1
U
U
51
85
4,8
U
20
10
33
U
U
U
H 12043;, ,;
•Qf WIST Arab-
__JJ!
u
y
, U
,; H
II IMMIr- ,^l M.IM-ll-
y
u
..M,-
M
,,r-,,,M,V,,,,.
M
1^,,
M
.,., ,u
, W
,.,tf
,,,..,y
,,.,..u. ......
u
u
%
Diff.
6.7
98
Results are in part per billion by volume (ppbv)
U = None detected
% Diff. = percent difference
Results in the non-shaded columns are from en-site analysis
Results in the shaded columns are from laboratory analysis.
continued
o
D)
(A
0)
a
-------
Table 1. Comparison of October 2002 Analysis Results of Rose Hill Volatile Organic Compounds in Air (continued).
r>
co
Results are in part per billion by volume (ppbv)
U = None detected
% Dtff. = pe'cent difference
Results in the non-shaded columns afe from on-site analysis.
Results in the shaded columns are from laboratory analysis.
Sample Number
Sample Location
Dichlorodifluoromethane
Dichloroletrafluoroethane
Vinyl Chloride
Chloroethane
Trichlofofluoromelhane
Isopropyl Alcohol
Acetone
1,1-Dichloroethene
Methylene Chloride
trans-1 2-Dichloroethene
Haxane
1,1-Dichloroethane
2-Butanone
cis-1 ,2-Dichloroethene
1,1,1-Trichforoethane
Cyclohexane
Carbon Tetrachloride
1 ,2-Dichloroethane
Benzene
Heptane
Trichloroethene
1 ,2-Dichloropropane
Toluene
Tetracnloroethene
Chlorobenzene
Ethylbenzene
m&p-Xylenes
o-Xylene
Styrene
4-Ethyltoluene
1 ,3,5-Trirrethvlbenzene
1 2,4-Trirretnvlbenzene
" ,3-Dichlorobenzere
1 ,4-Dichlorobenzene
• ,2-Dichlorobenzene
13497 j
Grid 137Amb. D.
U
U
U
U
U
U
19
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
11
19
U
U
4.7
U
8.1
U
U
U
12944
'•Or'id^Amb. :
,„,-„ M,,V -,-,-,-•
U
„ ....M,,,,,..,,,.
u
,,n,,n,,,,Mn,,,M,H,-
..nuMnnMn,,,,,,,,,,;
7& ,
U
„-„„„,„;!£„„„„„•
, u, , .'
,11,,,imi,IIM, :
,,,,M,,,,,M,,,-n,-M,/
.•„,¥,„. „
y
U, ,
ril -M,,-, ,-
V
u
, y
u
.,,. M,.,. -„
M,,,
2,5
U
U
u
,u
u
u
u
u
u
u
u
u
%
Diff.
295
13496
Grid 139
5SO
U
U
980
68
U
U
U
U
12
3200
U
U
57
U
3000
U
U
2300
2700
57
U
1800
31
220
2800
3700
1100
U
1000
470
930
U
23
U
,,,,, ,,1/294*, ,.,„.,
_ iiMQndm iti
, m ,„„
71
,,,.„ ,m
,„„, m
„„„,„ uiw „
nnnnnrM,,,,-,,,,,,
,„ , ,#„„„„„„
, .-unnV-,,,,,,, :
,,1111^1I ,
„ r,,,,,,,,^,,,,,,,,,,
.nnnn^Wn.nn,
31 ,
,,,,,,,,MW,,, , -
„- ft ,
,„. Mri,,.,,,,,
1900
, , y ,, ,
, U
.rnn.^O,,,,,-,-
„„,„„£»», ,
197
, ,„,,„„" ,,,,,„
1400
,.,,,,,,,32,,, .„„.
190
2600
3$00. ,
1100,
, , ,-57.. -„,
920
450
9SO
U
27
U
%
Diff.
32
11
2.9
3.1
24
37
36
15
18
22
29
14
7.1
5.4
0.0
8.0
4.3
3.2
17
13495
Grid 140
43
38
300
99
U
U
U
U
U
U
850
U
U
U
U
990
U
U
200
1100
U
u
83
U
U
1400
550
320
U
170
130
220
U
29
U
12946 , t
iuQrtd140iin ,
.$», „„.,„,
, A,.,,,,-
-„„,, u,?ff* ,„-,-,'
..M ,-'
nun, -,„#-„„„ ,-!
,, „,„ MUM,,,,,,
,„ ,,,^, „,„„„;
: M
nM.u.nMn.Mnn,'
U
930
; U
,n,u, „„«„,„„„-,
I.I.MM.IM^ftlMnu,.,,
m .,,.
!,,,,,,,-,,,,M-, -„,-„•
lt,Mn
,,. ,,,,^&r ,.
,1«qo
,..,„,., M,.,,,
- ,.«5,.,1,
.MMMUr.M,,,,-,,,,,,
,,,„ ,,M.,.. , , ,.
,,M,,M-,VKfl,,-,,,
-,,- W, r,-,
300
„„.. -,u
120
„ ,P3i., , .-.
ISO
U
30
u
%
Diff.
70
53
33
71
94
28
30
9,1
22
0.0
9.1
6.3
29
36
32
3.4
o
CO
CD
continued
-------
Table 1. Comparison of October 2002 Analysis Results of Rose Hill Volatile Organic Compounds in Air (continued).
Sample Number
Sample Location
Dichlorodifluoromethane
Dichlorotetrafluoroethane
Vinyl Chloride
Chloroe thane
Trichlorofluoromethane
Isopropyl Alcohol
Acetone
1 ,1-Dichloroethene
Methylene Chloride
trans-1 ,2-Dichloroethene
Hexane
1,1-Dichlorcethane
2-Butanone
cis-1 ,2-Dichloroethene
1 ,1,1-Trichloroethane
Cyclohexane
Carbon Tetrachloride
1 ,2-Dichlorcethane
Benzene
Heptane
Trichloroethene
1 ,2-Dichlorcpropane
Toluene
Tetrachloroethene
Chlorobenzene
Ethylbenzene
m&p-Xylenes
o-Xylene
Styrene
4-Ethyltoluene
1 ,3,5-Trimethylbenzene
1 ,2,4-Trimethylbenzene
1 ,3-Dichlorobenzene
1 ,4-Dichlorobenzene
1 ,2-Dichlorobenzene
13494
Grid 131
55
25
120
1800
U
U
U
16
U
U
2600
1000
U
55
910
3100
130
U
810
4400
U
U
520
U
U
3500
4600
1200
U
990
490
1300
U
100
U
1?947 „,„„
9Hd,131
,,,,-M,«ft,,,m,n,
,,,,m,M,^,m,,,,,i
u,m,,,T?Rn „,.,,„
•„,-„„ Ji*99.-,,,,
„„„,,,,¥,„„ ;
mil,,MllllIin,i
y
.MM.unuk,,,,,,,-,:
, 32,,,. ,
•m,,,r,M,,MmM,,,"
:„ »„,,,„.
6^0
U
,„??
580 ,,:
„„:(«$ .,i
•„,,,,, ..Mn-nnn.n
U ,
, 580 . =
rll ...JZffP :
• ,3?, :
L U
H,,,,,^,,,,,,,,,,,'
,„ , , ,,U. ,,,,„„;
,,,,,,,-M „„-„„•„
4009
, 1100
1lu.I1, „-
750,, ,,v
,.,-, *&..,„,„
w,,....
--,M- ,n ,
, ,,,120, .,„
tewm&tw-
%
Diff.
9.1
16
42
22
3.8
38
5.5
36
55
28
16
12
17
13
8.3
21
8.2
7.7
20
13493
Grid 80
74
U
290
430
77
670
650
U
U
14
900
U
790
94
U
1200
U
U
360
2200
25
U
3400
17
U
2600
4300
1600
U
760
370
840
U
31
U
12943
GddSO
86 ,
„ -,,,M ,
, lin,m,
-399
,„„„„„&&,-,„„„,
,lllli;33fli „,,,
, „ MuffiS!,,,,-,,, ,
...N.,,, „
„ ,y,,MM ,,
, ,„ H „„„„,.„
- m ,„,
, ,,,l,^, „„„„„,
, n,,,,,,^,,,,,,,,,
,llllllrll,?7, ,
,M,,,,,,,,nV,,,,m,,,
„,,„, „,#&„,•„„„
,„„-„„„«,„„„„,,
,„„-,„„ |U, ,,„„„„
„ ,-• , ,,2|50,,, „,, ,
.,,,.., ,21CX3.iniltI.
,,M HIM, !$„„„„,
,„„„„„ m.,,M
, MQ,,m-,,
.„„, J4., ,,„„,„,
..V!,,,,-,,,,,
.,. W,,,-,,-,
M,,!""^-, ••••
, , i1^00 ., •,
, , ,,M ••„„•
630
, 350 , ,
530
,.. V- ,. ,
,,,. ...34 ,.,.,.,
U
%
Diff.
19
14
9.3
6.5
51
15
8.9
27
3.2
53
28
4.5
20
5.9
12
12
19
17
5.4
1.2
9.7
13492
Grid 146
34
U
650
4000
U
U
34
U
U
35
83
670
14
100
U
1BO
U
12
250
52
U
U
60
U
38
91
170
170
U
71
31
91
U
10
U
12349
iiiim$rtd146imiii
„„„„„„*!*,
iiiiniiiiitirlitiiimiitlii
„„„.,„$$,„.,„„
4000
„„ .fo,,,,,,,,,
,,M,,, „,,
u
v
73-
..nmuSW,,,,,,,,,,,
>,.„.„„„.#;.„.„,.„
, M,,,,,,,?,^?!,.,, . , ,
1,!^llimiI1,.I,
, I.M.MI ..ft?,,,!...!..,,,
^ '
„., ,,,rV,n,m „„
40
„„„„„, M.n.nn,,,
, .....u,,-,,,-,--,
,. ,,86,,. .,,.,,
-,„•,•„«„„•,--,,
U ,.,.,
,,, ,„«,„,..•-,,
U, ,.,..„..
U
..p,, -.,„,,
• u •
%
Diff.
29
23
0.0
12
3.0
10
13
24
5,3
49
Results are in part per billion by volume (ppbv)
U = None detected
% Diff. = percent difference
Results in the non-shaded columns are from on-site analysis.
Results in the shaded columns are from laboratory analysis.
o
D)
(A
0)
continued
a
-------
Table 1. Comparison of October 2002 Analysis Results of Rose Hill Volatile Organic Compounds in Air (continued).
r>
tn
Results are in part per billion by volume (ppbv)
U = None detected
% Diff. = percent difference
Results in the non-shaded columns are from on-site analysis.
Results in the shaded columns are from laboratory analysis.
o
CO
CD
Sample Number
Sample Location
Dichlorodifluoromethane
Dichlorotetrafluoroethane
Vinyl Chloride
Chloroethane
Trichlorofluoromethane
Isopropyl Alcohol
Acetone
1,1-Dichloroethene
Methylene Chloride
trans-1 ,2-Dichloroethena
Hexane
1,1-Dichloroethane
2-Butanone
cis-1 ,2-Dichlcroethene
1,1 ,1-Trichloroethane
Cyclohexane
Carbon Telrachloride
1 ,2-DichloroetKane
Benzene
Heptane
Trichlorcethene
1 ,2-Dichloropropane
Toluene
Tetrachloioethene
Chlorobenzene
Ethylbenzene
m&p-Xylenes
o-Xylene
Styrene
4-Ethyltoluane
1 .3 5-Trimethylbenzene
1 ,2 4-Trimethylbenzene
1 ,3-Dichlorobenzene
1 ,4-Dichlorobenzene
1 .2-Dichlorobenzene
13490
LFG7
U
U
U
U
U
U
7.6
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
12955
PW7
, , ,y
, , M,,,,,,,,M,"
,,-.,M-,-,,M, •„„-„•
ll,ln,,,rIMl,,,,,
,,11I11T1,.mM. „•
,,,„ V,,,,,,,,,,,,,
, ..-.nJS, ,.„„„.
M ,„
14
., ,,,V! „„,
„ .....JU, „„,,„„
.,,,„ V!,,,.
,„„, ,M. ,..„
U „,„
•u ,-,,-," ,-,„•„-,
U
.I.,11MI.1,M ,
,,,„„,„$,„„-,„„•.
,„„ ,,H ,„„
,- M.m.VmrM,,,,,,
M,,mmn-,M ,,,„'„,„
, ,„„,-¥„-„-,-„„•
M,m,,,-M,,
i-MMM-M-,",,,,,,,,-
,,„„„,.-,#,„.,"„
.........y, „-,.
U
U
M . , .,
U
U
U
U
, --.,y ,., • ,-
U
%
Diff.
71
13489
LFG24
4.8
U
U
U
U
U
U
4.9
U
U
U
6.4
U
230
76
U
12
U
U
U
130
U
U
U
U
U
U
U
U
U
U
U
U
U
J
12956
WV24
6,J, ,,.„,,.
, , UM. ,„„,,
,,, ,M ,„,,„
,,.„.,«
M „„
„.„.«..„,..„,.
1,9, .•
,*^,TIIII;I,
,.„ l,,,^,-,,,,
„ in,,,^, „„
,,,,.;,„«,. ;„„
s,1lm.
,11Illl,w.. ,,.,
2ft,,.,,,
[lllliri^..
,,„,,.«„
M, ,-, ,„
„„,«.„„„.,
u
,,-..,„,,«..,-, --,
n,,-,,,^,1,?,,,,,,,,-,,,
..,,.,•„,.,».,.,:,...
M,u n ,
,.„ ,„«,,„„,,,
U
, „, u,.,,,,,,.
U
u.,
u
.Nu,..
u
u
u
u
u
%
Diff.
27
12
20
17
26
15
13488
LFG1
11
U
U
U
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
12957
, .Ml.l.^. •
13
^3
U
U
„-,„„!!*„„,,„„.
M
„,.„„„«,-„.-,,
u
U
M
y
,,,,, tf
,,-, .Mr,,-,,,,
„,, V
U
„ ,,,,«-,„„.,-
u
M
u
, , -,v, ....
u
y
u
%
Diff.
18
continued
-------
Table 1. Comparison of October 2002 Analysis Results of Rose Hill Volatile Organic Compounds in Air (continued).
O5
Sample Number
Sample Location
Dichlorodifluoromethane
Dichlorotetrafluoroethane
Vinyl Chloride
Chloroethane
Trichlorofluoromethane
Iscpropyl Alcohol
Acetone
1 , 1 -DichlcroetheTie
Methylene Chloride
trans-1 ,2-Dichloroethene
Hcxane
1,1-Dichloroethane
2-Butanone
cis-1 ,2-Dich!oroethene
1 1,1-Trichloroethane
Cyclohexane
Carbon Tetrachloride
1 ,2-Dichloroethane
Benzene
Heptane
Trichloroethene
1 ,2-DichloroproDane
Toluene
Tetrachloroethene
Chlorobenzene
Ethylbenzene
m&p-Xylenas
o-Xylene
Styrene
4-Ethyltoluene
1 ^S-Tri methylbenzene
1 ,2,4-Trimethylbenzene
1 ,3-Dichlorobenzene
1 ,4-Dichlorobenzene
1 ,2-Dichlorobenzene
13487
Grid 9
490
130
U
19
U
U
43
U
U
U
180
6.1
U
9.3
U
iro
u
U
250
420
U
U
24
U
640
790
650
130
U
230
220
370
U
45
31
12950
Grids-'
590
W
22
,,,n,A-M, n
^
M
n,,,-,,,,,^,,,, „-,„
,„ ,•„•,, M, „,„ u,
„,.. M „„
MM, , ,,U ,
i6q-
,,•„„-, -,V, ,.„-,„-,
'„„, ,,,,-M-,, ,-,
„ „„,„?£,,„„,„
„., n,M,M,,,,M,n
,,l,;,,,Mn»,»,:,
y
,, ,,y , „
, I1,M.,,17|0.I.
34S
, , u
', n, U
,,-,,-,,-,^ , ,, , ,
•„,•„„ •**•,,•
, , 6?°
790
030
1.ffl
„.,„. V
, ,,,-,1i50- ,-,
170
340
U ,
3S
26
%
Diff.
20
23
11
112
11
5.4
43
32
19
21
3.1
0.0
31
15
35
23
8.1
16
16
13486
Grid 9Amb
U
U
U
u
u
u
5.3
U
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
u
5.7
u
u
u
,13951, ,,,„
Grid's Amii,1 "
u
u
y
,,,,,,,,,A? •„,,„-.
y
M
„„ , ^Mlll .:
,,, H , „,,,„•
,,,[lll,,j17 „,
, , „ , M. . i , .. ,
y
u
„ , n.nVun, „,„
,-,„,-, M,,,, „•,„
,,,r,,,,,,M, ,„•„.„;
If ,
M , , •
„ ., , tf,,.,,,,,1
Jj,,, ;
T,T M ,-,, ,
.&„. .;
U
„,,.., ,,2.1,,,, .„.
, y
u,u. , „
, -,,,,,,1^.
1,4
U
.,, ,U., ,.„
U
u
--,--,, V-, , ,,-
„ .., w ..... ,
u
u
%
Diff.
806
13483
Grid 1 5A
30
U
U
56
U
U
U
U
U
U
U
51
U
U
U
19
U
U
U
U
U
40
130
U
10
14
U
U
U
23
15
33
U
23
U
129S4
""'.'•csMJfp,11;,1,1.
, M^?, ,
, , ,M „, ,
^
,„;$,„„„„„„
•£$
Vu
nn-n,,,,^,,,-,,,,,,,
„ MM, ,,M-,,,,r,,,,
„. M,,,,,,,,,,
1M^1M ,
u
, •„, „&„„„,„;
,„ ,Mn MM ,
„„,„, w,,, ,„
, M ,,M, ,„ , ,
„„„„, -,!!?„„,-„„,
• ^
„ ,„ ^ „
, ,,,1^
u
llni$,1
^7
r, ^n , „
srs
, M M,,
,, -if?-,,,-,,,-
,--„„••, 2,. ,.„
U
. , .. ,u,,. . ,
„ ;M •„-,., ,
,•„,, ,,W, „,-, ,
. 4r^r
• ,, n,^,,,,,- ,
,,-,,?f „,,, ,
u
%
Diff.
13.3
27
11
33
30
69
86
13
Results are in part per billion by volume (ppbv)
U = None detected
% Diff. = percent difference
Results in the non-shaded columns are from on-site analysis
Results in the shaded columns are from laboratory analysis.
continued
o
D)
(A
0)
a
-------
Rose Hill, Rl
Table 1. Comparison of October 2002 Analysis Results of Rose Hill Volatile Organic Compounds in Air (concluded).
Sample Number
Sample Location
Dichlorodrfluoromethane
Dichlorotetrafluoroethane
Vinyl Chloride
Chloroethane
Trichlorofluoromethane
Isopropyl Alcohol
Acetone
1,1-Dichloroethene
Methylene Chloride
trans-1 ,2-Dichloroethene
Hexane
1,1-Dichloroethane
2-Butanone
cis-1 ,2-Oichloroethene
1,1 ,1-Trichloroethane
Cyclohexane
Carbon Tetrachloride
1 ,2-Dichloroethane
Benzene
Heptane
Trichloroethene
1 ,2-Dichloropropane
Toluene
Tetrachloroethene
Chlorobenzene
Ethylbenzene
m&p-Xylenes
o-Xylene
Styrene
4-Ethyltoluone
1 ,3,5-Trimethylbenzene
1 ,2,4-Trimethylbenzene
1 ,3-Dichlorobenzene
1 ,4-Dichlorobenzene
1 ,2-Dichlorobenzene
13485
Grid 16
U
100
U
U
U
U
U
U
U
U
710
U
U
U
U
620
U
U
130
1100
U
U
31
U
800
1300
1300
74
27
1600
810
1300
73
200
64
•..,,,. ,!»»?,. , „,
GrkMB
•„,„,,„ y,,,,
130
: M
i.M.MM.Mn „ M
„, , ...iff,. , „ ,
JM,,,,,,,II,W,, cm,
;,,,M,M,,-M,,,,- -, ,
•..„ ,y., ,..,....
, M,
u
670
MMMrUM.rUH.MM., M1
, U
,„„ M
u
350
U :
„ ,,u, ,;
, 94 .
m „•
u
,,1M. ,«,„„„„,„•
,„ ,„ 18 .
U
, „ 730 ,
, 13P° u ,'
,„ .W ,.„.,„
,..51, ...„„..„
..., .....w
1400
780
1400
90
, 250
74
%
Diff.
30
5.6
44
28
19
42
8.8
0.0
0.0
31
13
3.7
7.7
23
25
16
13484
Grid 16 Dup.
90
110
U
U
U
U
U
U
u
u
750
U
U
4.3
U
660
U
U
140
1100
U
U
30
U
820
1400
1400
76
U
1700
860
1400
79
210
66
,. i.^Qsa
Grid 16 Dup,
M
W
,,„„ M
MMMM ,,M „ „,
^f
1^
u
V
M.M,,,,,,^,,, ,' ,
V
Ml 7*?
u
- , M ,
L , UlM
\l
350
U
.,.,..„«,.'„...,.
23
, «W ,
U
•,•„„,„„[•?,„„„„„„
i^f
u
719,
f300
ir-l 139°, ,„•
$2
U
1400
750
1300
80
240
S9
%
Diff.
1.3
47
30
13
40
13
7.1
71
32
18
13
7.1
1.3
14
4.5
Results are in part per billion by volume (ppbv)
U = None detected
% Diff. = percent difference
Results in the non-shaded columns are from on-site analysis.
Results in the shaded columns are from laboratory analysis.
C-7
-------
Table 2. Comparison of October 2002 Analysis Results of Rose Hill Fixed Gases.
Sample Number
Sample Location
Oxygen
Nitrogen
Melhane
Carbon dioxide
13500
Grid 137
1.3
48
57
40
mri| 12941
, Qtfd 13T
,- „.,„.&!?,„,„„
.ja
5?
42
%
Diff.
85.4
75.0
1.8
5.0
13499
Grid 1 37 D.
0.68
2.4
59
42
uiii ,1i?942 iirm
Grid1 ^Bup,
,.,.,,-W
e^,.
S6
42
%
Diff
66.2
67.1
5.1
0.0
13498
Grid 137Amb.
21
75
0.11
0,099
u a , „$¥?„,„ „„
iiQrtii('137^rrifc ,
30, .„„
7?
, „-„ , MM ,„„„,
U
%
Diff.
4.9
2.6
Sample Number
Sample Location
Oxygen
Nitrogen
Methane
Carbon dioxide
13497
Grid 137 Amb. D
21
77
U
0.035
12844
GtRMSTAmb,
20
r«
u
u
%
Diff.
4.8
1.3
13495
Grid 139
0.57
2.0
59
43
12$46
GtfcnaS
U- ,
Q.31
S3
43
%
Diff.
84.5
5.1
0.0
13495
Grid 1 dO
1.4
42
25
29
12946
Sffdt40
1J&
44
23
31
%
Diff.
28.6
4.B
8.0'
6.9
oo
Sample Number
Sample Location
Oxygen
Nitrogen
Methane
Carbon dioxide
13494
Grid 131
0.70
68
55
41
1ZS47 j
Grid T3t %
I Diff.
• , , U, , i
J
5.2 , j 23.5
1
, , ,,33 ...,- -I 3-6
43 | 4.9
13493
Grid 80
1.2
21
44
34
12948
Qrtd&i,.
0,38
1S
,43
38
%
Diff.
683
9.5
2.3
11.8
13492
Grid 146
5.3
67
7.8
16
,1,3MB
<3rt
-------
Table 2. Comparison of October 2002 Analysis Results of Rose Hill Fixed Gases (concluded).
Sample Number
Sample Location
Oxygen
Nitrogen
Methane
Carbon dioxide
13490
LFG7
20
77
U
0.82
12955
J%7
1B „
92
,. .„ U ,
13
%
Diff.
5.0
6.5
829
13489
LFG24
20
77
U
089
1295$
, Hv'34'
M ,,3ft,M,M, „
SO
, , „ ,-¥„„„,„
1,3
%
Diff.
0.0
3.9
34.3
13488
LFG1
19
77
U
,3
;;•*;; ^SZasftsf;-;::'
£>wi
,. T11Jj. llllllrl
f , -83 , , ,
„, ,M .,
: 3.G
%
Diff.
5.3
7.8
30.4
Sample Number
Sample Location
Oxygen
Nitrogen
Methane
Carbon dioxide
13487
Grid 9
2.1
65
11
20
129SO
Grid 9
0,97
6&
11
24
%
Diff.
538
1.5
0.0
200
13486
Grid 9 Amb
21
77
U
0.038
12951
Grid 9 Amb,
2£>
32
U
U
%
Diff.
4.8
6.5
13483
Grid 15A
2.9
77
0.083
16
12954
Grid15A
1.8
id
U
»
%
Diff.
44.8
2.6
31.3
r>
Sample Number
Samole Location
Oxygen
Nitrogen
Methane
Carbon dioxide
13485
Grid 16
2.3
3.7
60
33
• .R852;,.
<3rW16
U. „,.
, ,1-^,, , • '
65, .
33
%
Diff.
839
5.0
15.2
13484
Grid 16 Dup.
063
2.8
66
37
„, •-,1,29^lnll,
Gr|d15Dup.
0.^0
1.&
63
38
%
Diff.
52.4
35.7
4.5
2.7
Results are in percent by volume (%/'v)
U = None detected
% Diff = percent difference
Results in the non-shaded columns are from on-site analysis.
Results in the shaded columns are from laboratory analysis.
Average results from the replicates of the on-site analyses are entered here.
-------
A Case Study
C-10
-------
Rose Hill, Rl
Appendix D
LandGEM Model Runs
D-l
-------
A Case Study
Contents
Table D-l. Northern Parcel Methane Emisson Rate from Year 1968 to 2203 D-3
Table D-2. Northern Parcel NMOC Emission Rate from Year 1968 to 2203 D-7
Table D-3. Northern Parcel 1,1,1-Trichloroethane Emission Rate from Year 1968 to 2203 D-ll
Table D-4. Northern Parcel Benzene Emission Rate from Year 1968 to 2203 D-15
Table D-5. Northern Parcel Chlorobenzene Emission Rate from Year 1968 to 2203 D-19
Table D-6. Northern Parcel Chloroethane Emission Rate from Year 1968 to 2203 D-23
Table D-7. Northern Parcel Dichlorobenzene Emission Rate from Year 1968 to 2203 D-27
Table D-8. Northern Parcel Toluene Emission Rate from Year 1968 to 2203 D-31
Table D-9. Northern Parcel Trichloroethene Emission Rate from Year 1968 to 2203 D-35
Table D-10. Northern Parcel Vinyl Chloride Emission Rate from Year 1968 to 2203 D-39
Table D-ll. Northern Parcel m,p-Xylene Emission Rate from Year 1968 to 2203 D-43
Table D-12. Northern Parcel o-Xylene Emission Rate from Year 1968 to 2203 D-47
Table D-l3. Southern Parcel Methane Emisson Rate from Year 1968 to 2203 D-51
Table D-14. Southern Parcel NMOC Emisson Rate from Year 1968 to 2203 D-55
Table D-15. Southern Parcel Benzene Emission Rate from Year 1968 to 2203 D-59
Table D-16. Southern Parcel Chlorobenzene Emission Rate from Year 1968 to 2203 D-63
Table D-17. Southern Parcel Chloroethane Emission Rate from Year 1968 to 2203 D-67
Table D-18. Southern Parcel Dichlorobenzene Emission Rate from Year 1968 to 2203 D-71
Table D-19. Southern Parcel Toluene Emission Rate from Year 1968 to 2203 D-75
Table D-20. Southern Parcel Trichloroethene Emission Rate from Year 1968 to 2203 D-79
Table D-21. Southern Parcel Vinyl Chloride Emission Rate from Year 1968 to 2203 D-83
Table D-22. Southern Parcel m,p-Xylene Emission Rate from Year 1968 to 2203 D-87
Table D-23. Southern Parcel o-Xylene Emission Rate from Year 1968 to 2203 D-91
D-2
-------
Rose Hill, Rl
Table D-1. Northern Parcel Methane Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000\030177~1.002\ROSEHI~l\NORTHERN.PfiM
Model Parameters
Lo : 170.00 wA3 / Mg ***** user Mode Selection H
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 4500.00 ppinv ***** user Mode Selection *<
Methane : 56.0000 % volume
Carbon Dioxide : 44.0000 4 volume
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Year Refuse In Place [Mg)
1968 1.318E+04
1969 2.636E+04
1970 3.954E+04
1971 5.272E+Q4
1972 6.590E+04
1973 7.908E+Q4
1974 9.226E+04
1975 1.054E+05
1976 1.1B6E+05
1977 1.31SE+05
1978 1.450E+OS
1979 1.5B2E+05
1930 1.713E+OS
1981 1.845E+05
1932 1.977E+05
1983 1.977E+05
1984 1.977E+05
1985 1.977E*05
1986 1.977E-HD5
1937 1.977E+05
1988 1.977E+Q5
1939 1.977E+05
1990 1.977E+05
1991 1.977E+05
1992 1.977E+OS
1993 1.977E+05
1994 1.977E+05
1995 1.977E+05
1996 1.977E+05
1997 1.977E+05
1998 1.977E+05
1999 1.977EH-05
2000 1.977E+OS
2001 1.977E+05
2002 1.977E+05
2003 1.977E+05
2004 1.977E+05
2005 1.977EJ-05
2006 1.977E+05
2007 1.977E+05
2008 1.977E+05
2009 1.977E+05
2010 1.977E+05
2011 1.977E+05
2012 1.977E+05
2013 1.977E+05
2014 1.977E+05
Methane Emission Rate
[Mg/yr) [Cubic m/yr)
7.474E+01
1.458E+02
2.135E+02
2.778E+02
3.390E+02
3.972E+02
4.525E+02
5.052E+02
5.553E+02
6.030E+02
6.483E+02
6.914E+02
7.324E+02
7.714E+02
8.036E+02
7.691Et02
7.316E+02
6.959E+02
6.620E+02
S.297E+02
5.990E+02
5.698E+02
5.420E+02
5.156E+02
4.904E+02
4.665E+02
4.437E+02
4.221E+02
4.015E+02
3.819E+02
3.633E+02
3.456E+02
3.287E+02
3.127E+02
2.975E+02
2.829E+02
2.691E+02
2.560E+02
2.435E+02
2.317E+02
2.204E+02
2.096E+02
1.994E+02
1.897E+02
1.804E+02
1.716E+02
1.632E+02
1.120E+05
2.186E+05
3.200E+05
4.164E+05
5.081E+05
5.953E+05
6.783E+05
7.573E+05
8.324E+05
9.038E+05
9.717E+OS
1.036E+OS
1.098E+06
1.156E+06
1.212E+06
1.153E+06
1.097E+06
1.043E-I-06
9.923E+05
9.439E-t-05
8.978E+05
8.541E+05
8.124E+05
7.728E+05
7.351E+OS
6.992E+05
6.651E+05
6.327E+05
6.018E+05
5.725Et05
5.446E+05
5.180E+05
4.927E+05
4.687E+05
4.459E+05
4.241E+05
4.034E+05
3.B38E+-05
3.650E+05
3.472E+05
3.303E+05
3.142E+05
2.989E+05
2.343E+05
2.704E+OS
2.572E+05
2.447E+05
D-3
-------
A Case Study
Table D-1. Northern Parcel Methane Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2026
2029
2030
2031
2032
2033
2034
2035
2036
203?
2038
2039
2040
2041
2042
2043
2044
2045
2046
2047
2Q4B
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2-075
2076
2077
2078
2079
2030
2081
2032
20B3
2034
2085
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1-977E+05
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-I-05
1.977E+05
1.977E+05
1.977E+05
1,977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1 .977E+05
1.977E+05
1.977E+OE.
1.977E+05
1.977E+05
1.977E-I-05
1.977E+05
1.553E+02
1.477E+02
1.405E+02
1.337E+02
1.271E+02
1.209E+02
1.150E+02
1.094E+02
1.041E+02
9.901E+01
9.419E+01
8.959E+01
S.522E+01
8.107E+01
7.711E+01
7.335E+01
6.977E+01
6.637E+01
6.313E+01
6.D06E+01
5.713E+01
5.434E+01
5.169E+01
4.917E+01
4.677E+01
4.449E+01
4.232E+01
4.026E+01
3.829E+01
3.643E+01
3.465E+01
3.296E+01
3.135E+01
2.932E+01
2.837E+01
2.698E+01
2.567E+01
2.442E+01
2.323E+01
2.209E-I-01
2.102E+01
1.999E+01
1.902E+01
1.809E+01
1.721E+01
1.637E+01
1.557E+01
1.431E+01
1.409E+01
1.340E+01
1.275E+01
1.212E+01
1.153E+01
1.097E-I-01
1.044E+01
9.927E+00
9.443E+00
8.932E+00
8.544E+00
S.128E+00
7.731E4-00
7.354E+00
6.995E+00
6.654E+00
6.330E+00
6.021E+00
5.727E-I-00
5.44SEtOO
5.182E+00
4.930E-I-00
4.689E+00
2.326E+05
2.214E+05
2.106E+05
2.003E+05
1.906E+05
1.813E+05
1.724Et05
1.640E+05
1.560E+05
1.484E+05
1.412E+05
1.343E+05
1.277E+05
1.215E+05
1.156E+05
1.099E+05
1.046E+05
9.949E+04
9.463E+04
9.002E+04
S.563E+04
8.145E+04
7.748E+04
7.370E+04
7.011E+04
6.669E+04
6.343E+04
6.034E+04
5.740E+04
5.460E-1-04
5.194E+04
4.940E+04
4.699E+04
4.470E+04
4-252E+04
4.045E+04
3.847E+04
3.660E+04
3.431E-I-04
3.312E+04
3.150E+04
2.996E+04
2.850E+04
2.711E+04
2.579E+04
2.453E+04
2-334E+04
2.220E+04
2.112E+04
2.009E+04
1.911E+04
1.317E+04
1-729E+04
1.644E+04
1.564E+04
1.438E+04
1.41SE+04
1.345E+04
1.281E+04
1.218E+04
1.159E+04
1.102E+04
1-049E+04
9.974E+03
9.488E+03
9.025E+03
8.S85E+03
B.166E+03
7.768E+03
7.339E-I-03
7.029E+03
D-4
-------
Rose Hill, Rl
Table D-1. Northern Parcel Methane Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
CMg/yr)
(Cubic m/yr)
2086
2087
2088
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
2155
2156
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q6
977E+Q5
977E+OS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E-J-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
4.
4.
4.
3,
3.
3.
3.
3,
2.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
9.
e.
8.
7 .
7 ,
7.
6.
6.
6.
5.
5,
5.
4.
4.
4.
4.
4,
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
4S1E+00
243E+00
036E+00
839E+00
652E+00
474E+00
304E+00
143E+00
990E+00
844E+00
705E+00
573E+00
448E+00
329E+00
215E+00
107E+00
004E+00
906E+00
814E+00
725E+00
641E+00
561E+00
485E+00
412E+00
343E+00
278E+00
216E+00
156E+00
100E+00
046E+00
953E-01
467E-01
006E-01
566E-01
149E-01
751E-01
373E-01
014E-01
672E-01
346E-01
037E-01
742E-01
462E-01
196E-01
942E-01
701E-01
472E-01
254E-01
046E-01
849E-01
661E-01
433E-01
313E-01
151E-01
998E-01
852E-01
712E-01
580E-01
454E-01
335E-01
221E-01
112E-01
009E-01
911E-01
818E-01
730E-01
645E-01
565E-01
489E-01
416E-01
347E-01
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
. 636E+03
. 360E+03
. 050E+03
, 755E+03
.474E+03
-207E+03
. 953E+03
-712E+03
. 482E+03
.263E+03
. 055E+03
. 857E+03
.669E+03
-490E+03
.320E+03
.158E+03
-OQ4E+03
-858E+03
. 718E+03
.586E+03
. 460E+03
.340E+03
-226E+03
-117E+03
. 014E+03
. 916E+03
.822E+03
. 733E+03
-649E+03
.568E+03
.492E+03
. 419E+03
.350E+03
.284E+03
-221E+03
. 162E+03
. 105E+03
-051E+03
.OOOE+03
.512E+02
.048E+02
.607E+02
.187E+02
.738E+02
,408E+02
.047E+02
. 703E+02
.376E+02
-065E+Q2
. 770E+02
-488E+02
.220E+02
. 966E+02
.724E+02
.493E+02
.274E+02
.066E+02
.867E+02
. 679E+02
. 499E+02
-329E+02
. 166E+02
-012E+02
.865E+02
.725E+02
. 592E+02
.466E+02
.346E+02
-231E+02
. 122E+02
-019E+02
D-5
-------
A Case Study
Table D-1. Northern Parcel Methane Emisson Rate from Year 1968 to 2203 (concluded).
Year
Re/use In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2134
2185
2186
2187
2188
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-KJ5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.2B1E-01
1.219B-01
1.159E-01
1.103E-01
1.049E-01
9.979E-02
9.492E-02
9.029E-02
8.5B9E-Q2
8.170E-02
7.771E-02
"7.392E-02
7.032E-02
6.689E-02
6.363E-02
6.052E-02
5.757E-02
5.476E-02
5.209E-02
4.955E-02
4.714E-02
4.484E-02
4.265E-02
4-057E-02
3.859E-02
3.671E-02
3.492E-02
3.322E-02
3.160E-02
3.0QSE-02
2.859E-02
2.719E-02
2.587E-02
2.461E-02
2.341E-02
2.227E-02
2.118E-02
2.015E-02
1.916E-02
1.823E-02
1.734E-02
1.649E-02
1.569E-02
1.492E-02
1.420E-02
1.350E-02
1-285E-02
1.921E+02
1.827E+02
1.738E+02
1.653E+02
1.572E+02
1.496E+02
1.423E+02
1.353E+02
1.237E+02
1.225E+02
1.165E+02
1.108E+02
1.054E+02
1.003E+02
9.537E+01
9.072E+01
8-629E+01
8.209E+01
7.30SE+01
7.427E+01
7.065E+01
6.721E+01
6.393E-1-01
6.081E+01
5.784E+01
5.502E+01
5.234E+01
4.979E+01
4.736E+01
4.505E+01
4.285E+01
4.076E+01
3.377E+01
3. 638E+01
3.508E+01
3.337E+01
3.175E+01
3.020E+01
2.872E+01
2.732E+01
2.599E+01
2.472E+01
2.352E+01
2.237E+01
2.128E+01
2.024E+01
1.925E+01
D-6
-------
Rose Hill, Rl
Table D-2. Northern Parcel NMOC Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000\030177~1.002\ROSEHI~1\NORTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
fc : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 * volume
Carbon Dioxide : 44.0000 I volume
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year : 2003 Closure Year; 2004
Capacity : 137692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year : 13179,47 Mg/year
Model Results
Year
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1981
1932
19S3
19B4
1935
1986
19S7
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
2013
2014
Refuse In Place (Mg)
1.318E+04
2.636E+04
3.954E+04
5.272E+04
6.590E+04
7.908E+04
9.226E+04
1.054E+QS
1.1B6E+05
1.318E+05
1.450E+-05
1.5B2E+Q5
1.713E+-05
NMOC Emission Rate
[Mg/yr) (Cubic m/yr)
1.845E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
3.227E+00
6.296E+00
9.216E+00
1.199E+01
1.463E+01
1.715E+01
1.954E+01
2.131E+01
2.398E+01
2.603E+01
2.799E+01
2.935E+01
3.162E+01
3.331E+01
3.491E+01
3.321Et01
3.159E+01
3.005E-I-01
2.858E+01
2.719E+01
2.536E+01
2.460E+01
2.340E+01
2.226E+01
2.117E+01
2.014E+01
1.916E+01
.822E+01
.734E+01
.649E+01
.569E+01
.492E+01
1.419E+01
1.350E+01
1.2S4E+01
1.222E+01
1.162E+01
1.105E+01
1.051E+01
l.OOOE+01
9.514E+00
9.050E+00
8.609E+00
B.1B9E+00
7.789E+00
7.409E+00
7.048E+00
9.002E+02
1.757E+03
2.571E+03
3.346E+03
4.083E+03
4.784E+03
5.451E+03
6.085E+03
6.639E+03
7.263E+03
7.S09E+03
8.328E+03
8.822E+03
9.292E+03
9.739E+03
9.264E+03
8.812E+03
8.332E+03
7.974E+03
7.535E+03
7.215E+03
6.363E+03
6.528E+03
6.210E*03
5.907E+03
5.619E+03
5.345E+03
5.034E+03
4.836E+03
4.SOOE+03
4-376E+03
4.163E+-03
3.960E+03
3.766E+03
3.583E+03
3.408E+03
3.242E+03
3.084E+03
2.933E+03
2.790E+03
2.654E+03
2.525E+03
2.402E+03
2.235E+03
2-173E+03
2.067E+03
1.966E+03
D-7
-------
A Case Study
Table D-2. Northern Parcel NMOC Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2090
20B1
2032
2083
2084
2085
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E-I-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
917E+05
6.
&,
6.
5.
5.
S.
4.
4,
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7.
7.
7.
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
704E+00
377EH-00
066E+00
770E+00
489EfOQ
221E+00
967E+00
724E+00
494E-I-QQ
275E4-00
066E-I-00
868E+00
679E+00
50QE+OQ
329EtOO
167E+00
012E+00
866E4-00
726E+00
S93E+GQ
466E+00
346E+00
232E+00
123E+00
019E+00
921E+00
B27E-t-00
738E-I-00
653E+00
573E+00
496E+00
423E+00
354E+00
2BSE+00
225E+OQ
165E+00
108E+00
054E+00
003E+OQ
539E-01
073E-01
631E-01
210E-01
810E-01
429E-01
066E-01
722E-01
394E-01
082E-01
785E-01
503E-01
235E-01
980E-01
737E-01
506E-01
236E-01
077E-01
878E-01
689E-01
509E-01
338E-01
175E-01
020E-01
873E-01
733E-01
600E-01
473E-01
352E-01
237E-01
128E-01
025E-01
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
3
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
3
8
8
7
7
6
6
6
5
5
.870E+03
.779E+03
. 692E+03
. 610E+03
.531E-I-03
-457E+03
.336E+03
-318E+03
.254E+03
.193E+03
. 134E+03
-079E+03
. Q26E+03
-764E+02
.238E+02
.835E+02
-404E+02
. 994E+02
. 604E+02
-234E+02
. B81E+02
. 545E+02
,226E-K>2
-922E+02
. 634E+02
.359E-1-02
. 097E+02
. 349E+02
. 612E+02
.387E+02
.173E+02
-970E+02
.776E-H32
.592E+02
.417E+02
.250E+02
. 092E+02
. 941E+02
-798E+02
. S61E+02
.531E+02
. 408E+02
.290E-5-02
.179E+02
,072E+02
.971E+02
.875E+02
. 734E+02
. 697E+02
. 614E+02
-535E+02
. 460E+02
-389E+02
.321Et02
.257E+02
. 196E+02
.137E+02
.082E+02
-029E+02
. 790E+01
.312E+01
. 35SE+01
-426E+01
, 015E+01
. 624E+01
.252E+01
.899E-I-01
.562E+01
.242E+01
. 938Ef01
. 648Et01
D-8
-------
Rose Hill, Rl
Table D-2. Northern Parcel NMOC Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
CMg/yr)
(Cubic m/yr)
2086
2087
2088
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
2155
2156
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q6
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7 .
7,
7 .
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
9.
9.
8.
8.
7.
7 .
7 .
6.
6.
6.
5.
926E-01
832E-Q1
743E-01
658E-01
577E-01
500E-01
427E-01
357E-Q1
291E-Q1
228E-01
168E-01
111E-01
057E-01
005E-01
563E-02
097E-02
653E-02
231E-02
830E-02
448E-02
035E-02
739E-02
410E-02
098E-02
800E-02
518E-02
248E-02
992E-02
749E-02
517E-02
297E-02
037E-02
888E-02
699E-02
518E-02
347E-02
183E-02
028E-02
880E-02
740E-Q2
606E-02
479E-02
358E-02
243E-02
134E-02
030E-02
931E-02
837E-02
747E-02
662E-02
581E-02
504E-02
430E-02
361E-02
294E-02
231E-02
171E-02
114E-02
060E-02
008E-02
588E-03
12GE-03
676E-03
252E-03
850E-03
467E-03
103E-03
757E-03
427E-03
114E-03
815E-03
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
.373E+01
-111E+01
. 861E+01
. S24E+01
.399E+01
-184E+Q1
. 930E+01
.786E+01
. 601E+01
-426E+01
-259E+01
-100E+01
.949E+01
. 805E+01
. 668E+01
.538E+01
-414E+01
-296E+01
. 194E+01
-078E+01
. 976E+01
.880E+01
, 788E+01
-701E+Q1
. 618E+01
-539E+01
.464E+01
. 393E+01
-325E+01
.260E-t-01
.199E+01
. 140E+01
. 085E+01
.032E+01
9-815E+00
9
8
8
8
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
. 336E+00
. 881E+00
-448E+00
.036E+00
. 644E+00
-271E+00
. 916E+00
.579E+00
.258E+00
, 953E+00
.663E+00
. 387E+00
. 124E+00
-874E+00
. 636E+00
-410E+00
.195E+00
. 990E+00
.796E+00
. 611E+00
.435E+00
.267E-1-00
.108E+00
. 956E+00
. 812E+00
.675E+00
.544E+00
-420E+00
.302E+00
. 190E+00
. OS3E+00
. 982E+00
.385E+00
-793E+00
-706E+00
. 622E+00
D-9
-------
A Case Study
Table D-2. Northern Parcel NMOC Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
2188
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E-5-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+OS
977E+05
977E+05
977E+05
977E+-05
977E-1-05
977E+05
977E+05
977E+05
977E+05
5.
5.
5.
4.
4.
4-
4.
3-
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7.
7.
7 .
6.
6.
6.
5.
S.
532E-03
262E-Q3
005E-03
761E-03
529E-03
3QSE-Q3
098E-03
898E-03
708E-03
527E-03
355E-03
192E-03
036E-03
888E-03
747E-03
613E-03
486E-03
364E-03
249E-03
139E-03
Q35E-03
936E-03
641E-03
752E-03
666E-03
S85E-03
508E-03
434E-03
364E-03
298E-03
234E-03
174E-03
117E-03
OS2E-03
011E-03
613E-04
144E-04
698E-04
274E-04
870E-04
486E-04
121E-04
774E-04
444E-04
129E-04
830E-04
546E-04
1
1
1
1
1
1
1
1
1
9
9
8
8
8
7
7
6
6
6
5
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
.543E+00
-468E+00
.396E+00
. 328E+00
.264E+00
-202E+00
. 143E+-00
. 088E+00
. 034E+00
.840E-01
-360E-01
. 904E-01
.470E-01
.057E-01
. 664E-01
.290E-01
-934E-01
-59SE-01
.274E-01
. 968E-01
. 677E-01
.400E-01
-137E-01
-887E-01
. 648E-01
-422E-01
.206E-01
. 001E-01
.806E-01
. 620E-01
.443E-01
-276E-01
. 116E-01
. 964E-01
-8I9E-01
. 682E-01
. 551E-01
-427E-01
.308E-01
. 196E-01
. 089E-01
. 937E-01
. 690E-01
.798E-01
. 710E-01
.S27E-01
.547E-01
D-10
-------
Rose Hill, Rl
Table D-3. Northern Parcel 1,1,1,-Trochloroethane Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\NORTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 1 volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : 1,1,1-Trichloroethane (HAP)
Molecular wt - 133.41 Concentration - 0.580000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Year
Refuse In Place {Mg)
1,1,1-Trichloroethane (HAP) Emission Rate
(Mg/yr) (Cubic m/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 318E+04
. 636E+04
.954E+04
.272E+Q4
, 590E+04
. 908E+04
.226E+04
. 054E+05
. 186E+05
.318E+Q5
.450E+05
.5S2E+05
. 713E+05
.845E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
, 977E+Q5
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
.977E+05
6.
1.
1,
2.
2,
3.
3.
4.
4.
5.
5.
5.
6.
6.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4,
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
438E-04
256E-03
839E-03
393E-03
920E-03
421E-03
898E-03
352E-03
784E-03
194E-03
585E-03
956E-03
309E-03
646E-03
965E-03
626E-03
302E-03
995E-03
703E-03
425E-03
160E-03
908E-03
669E-03
441E-03
225E-03
019E-03
823E-03
636E-03
459E-03
290E-03
130E-03
977E-03
832E-03
694E-03
562E-03
437E-03
319E-03
205E-03
098E-03
996E-03
898E-03
806E-03
718E-03
634E-03
554E-03
1
2
3
4
5
6
7
7
8
9
1
1
1
1
1
1
1
1
1
9
9
G
S
8
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
. 160E-01
.264E-01
-314E-01
. 312E-01
-262E-01
.166E-01
. 026E-01
. 343E-01
. 621E-01
.361E-01
. 006E+00
.073E+00
.137E+00
. 19SE+00
.255E+00
. 194E+00
.136E+00
. 080E+00
, 028E+00
. 776E-01
-299E-01
. 846E-01
-414E-01
. 004E-01
. 613E-01
.242E-01
-889E-01
. 553E-01
-233E-01
. 929E-01
, 640E-01
.365E-01
.103E-01
. 855E-01
. 618E-01
.393E-01
. 178E-01
. 975E-01
.781E-01
.596E-01
. 421E-01
.254E-01
.Q95E-01
, 944E-01
. 801E-01
D-ll
-------
A Case Study
Table D-3. Northern Parcel 1,1,1,-Trochloroethane Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place JMg)
(Mg/yr)
[Cubic m/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1.
1.
1,
1,
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
9T7E+05
977E+Q5
977E+05
977E+05
977E+OS
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
917E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-I-05
977E+05
1.
1,
1.
1,
1.
1.
1.
1.
9.
9.
8.
8.
8.
7.
7.
6.
6.
6.
6.
5.
5.
5.
4,
4.
4.
4.
4.
3.
3.
3.
3,
3,
2.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
9.
9.
8,
8.
8,
7.
7.
7.
6.
6,
6.
5.
5.
5.
4.
4.
4-
478E-03
406E-03
33BE-03
272E-03
210E-03
151E-03
095E-03
042E-03
910E-04
427E-04
967E-04
529E-04
113E-04
718E-04
341E-04
983E-04
643E-04
319E-04
011E-04
717E-04
439E-04
173E-04
921E-04
681E-04
453E-04
236E-04
029E-04
S33E-04
646E-04
466E-04
299E-04
138E-04
985E-04
B39E-04
701E-04
569E-04
444E-04
325E-04
211E-04
103E-04
001E-04
903E-04
91QE-04
722E-04
638E-04
558E-04
482E-04
410E-04
341E-04
276E-04
214E-04
154E-04
098E-04
044E-04
935E-05
451E-05
990E-05
552E-05
134E-05
738E-05
360E-05
001E-05
660E-05
335E-05
026E-05
732E-05
453E-05
187E-05
934E-05
693E-05
464E-05
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
8
7
7
6
. S64E-01
-534E-01
.411E-01
-293E-01
.181E-01
-075E-01
. 974E-01
-877E-01
.7B6E-01
. 699E-01
. 616E-01
-S37E-01
.462E-01
-391E-01
. 323E-01
.259E-01
.197B-01
-139E-01
.Q83E-01
-030E-01
.301E-02
. 323E-02
-869E-02
-436E-02
.025E-02
. 633E-02
.261E-02
.907E-02
6-570E-02
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
3
.250E-02
. 945E-02
, 655E-02
. 379E-02
. 117E-02
-867E-02
. 630E-02
.404E-02
-189E-02
. 985E-02
. 791E-02
. 606E-02
.430E-02
-263E-02
.103E-02
-952E-02
. 808E-02
. S71E-02
.541E-02
-417E-02
.299E-02
-187E-02
.080E-02
. 979E-02
. B32E-02
-791E-02
. 703E-02
. 620E-02
.541E-02
-466E-02
.394E-02
-326E-02
.262E-02
-200E-02
. 142E-02
-086E-02
. QG3E-02
.S27E-03
.347E-03
-892E-03
-458E-03
-045E-03
D-12
-------
Rose Hill, Rl
Table D-3. Northern Parcel 1,1,1,-Trochloroethane Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
CMg/yr)
[Cubic m/yr)
2084
20BS
20B6
2037
2038
2089
2090
2091
2092
2093
2094
2095
209S
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-1-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
9.
9.
9.
8.
8.
7.
7.
7 .
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3,
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1,
1.
1.
1.
1.
1.
1.
1.
247E-05
039E-05
842E-05
65 5 E- 05
477E-05
307E-05
146E-05
993E-05
847E-05
708E-05
576E-05
450E-05
331E-05
217E-05
109E-05
006E-05
908E-05
815E-05
727E-05
642E-05
562E-05
4B6E-05
4 14 E- 05
345E-05
279E-05
217E-05
157E-05
1Q1E-05
047E-05
961E-06
475E-06
013E-06
574E-06
156E-06
758E-06
379E-06
020E-06
677E-06
352E-06
042E-06
747E-06
467E-06
200E-06
947E-06
705E-06
476E-06
25SE-06
050E-06
852E-06
665E-06
486E-06
316E-06
154E-06
OOOE-06
854E-06
715E-06
582E-06
456E-06
337E-06
223E-06
114E-06
011E-06
913E-06
820E-06
731E-06
647E-06
566E-06
49QE-06
417E-06
348E-06
282E-06
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
3
8
8
7
7
6
6
6
5
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
2
. 653E-03
.280E-03
. 925E-03
-537E-Q3
.266E-03
. 960E-03
.669E-03
.393E-03
. 130E-03
-330E-03
. 642E-03
. 415E-03
.200E-03
.995E-03
.800E-03
.615E-03
-439E-03
-271E-03
. 111E-03
. 960E-03
. 315E-03
.678E-03
.547E-03
. 423E-03
-305E-03
-193E-03
. 086E-03
. 984E-03
. 887E-03
.795E-03
-708E-03
-624E-03
.545E-03
. 470E-03
.398E-03
.330E-03
-265E-03
-2Q3E-03
.145E-03
. 039E-03
-036E-Q3
. 352E-04
.372E-04
. 915E-04
, 480E-04
.066E-04
. 673E-04
.299E-04
. 943E-04
. 604E-04
-282E-04
. 976E-04
. 684E-04
. 407E-04
.143E-04
.392E-04
. 654E-04
.427E-04
-211E-04
. 006E-04
. 810E-04
. 624E-04
-448E-04
.279E-04
. 120E-04
. 967E-04
. 823E-04
.635E-04
-554E-04
. 429E-04
.311E-Q4
D-13
-------
A Case Study
Table D-3. Northern Parcel 1,1,1,-Trochloroethane Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
21S1
2182
2183
21B4
2185
2186
2187
2188
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1,
1.
1.
977E+Q5
977E+OS
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+OS
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
917E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-I-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
1.
1.
1.
1.
9.
9.
9.
8.
8.
7,
7 .
7.
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
22QE-06
160E-06
104E-06
050E-06
987E-07
500E-07
037E-07
596E-07
177E-07
776E-07
399E-07
038E-07
694E-07
366E-07
057E-07
762E-07
481E-07
214E-07
959E-07
718E-07
4S7E-07
269E-07
060E-07
662E-07
674E-07
49SE-Q7
324E-07
162E-07
008E-07
SS1E-07
722E-07
589E-07
463E-07
343E-07
228E-07
120E-07
016E-07
916E-07
824E-07
735E-07
651E-07
570E-07
494E-07
421E-07
352E-07
286E-07
223E-07
163E-07
107E-07
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
8
7
7
6
6
6
5
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
2
2
2
1
. 198E-04
-091E-04
. 989E-04
.892E-04
.800E-04
, 712E-04
. 629E-04
-549E-04
.474E-04
-402E-04
-333E-04
.268E-04
.206E-04
-148E-04
. 092E-04
.Q38E-04
-878B-05
.396E-05
. 938E-05
-502E-05
. 087E-05
.693E-05
-317E-05
-9S1E-05
. 621E-05
.298E-05
. 991E-05
. 699E-05
-421E-05
. 157E-05
.905E-05
. 666E-05
. 438E-05
.222E-05
-016E-05
, 820E-05
-634E-05
.457E-05
-288E-05
, 128E-05
. 975E-05
. 830E-05
. 692E-05
.561E-05
,436E-05
.317E-05
-204E-05
. 096E-05
. 994E-05
D-14
-------
Rose Hill, Rl
Table D-4. Northern Parcel Benzene Emisson Rate from Year 1968 to 2203.
Source: H:\3000V030177~1.000\030177~1.OD2\ROSEHI~1\NORTHERN.PRM
Model Parameters
Lo s 170.00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 $ volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : Benzene (HAP/VOC)
Molecular wt - 76.12 Concentration - 1.640000 ppmV
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Year
Refuse In Place (Mg)
Benzene (HAP/VOC) Emission Rate
(Mg/yr) (Cubic m/yr)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1931
1982
1933
1984
19S5
1936
1987
1988
19B9
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
I
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
I
. 318E+04
. 636E+Q4
. 954E+04
.272E+04
.590E+04
. 9Q8E+04
.226E+04
. 054E+05
. 186E+05
. 318E+05
.450E+05
.5B2E+05
. 713E+05
.B45E+05
. 977E+Q5
. 977E+Q5
.977E+05
. 977E+Q5
.977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
, 977E+05
-977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
-977E+05
-977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
1.
2.
3.
3.
4.
5.
6.
7 .
7.
8.
9.
9.
1.
1.
1.
1.
1.
9.
9.
8.
8.
8.
7.
7.
6,
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
066E-03
OBOE-03
045E-03
962E-03
835E-03
665E-03
455E-03
206E-03
920E-03
600E-03
247E-03
8S2E-03
045E-02
100E-02
153E-02
G97E-02
044E-02
926E-03
442E-03
982E-03
544E-03
127E-03
731E-03
354E-03
995E-03
65 4 E- 03
329E-03
021E-03
727E-03
448E-03
182E-03
929E-03
689E-03
460E-03
243E-03
036E-03
839E-03
652E-03
474E-03
304E-03
143E-03
990E-03
844E-03
705E-03
573E-03
3
6
9
1
1
1
1
2
2
2
2
3
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
.281E-01
.401E-01
.370E-01
.219E+00
. 488E+00
. 743E+00
. 987E+00
.218E+00
-438E+00
. 647E+00
.846E+00
-035E+00
-215E+00
.3B6E+00
-549E+00
.376E+00
-212E+00
.055E+00
-906E+00
. 764E+00
. 629E+00
.501E+00
.379E+00
.263E+00
-153E+00
.048E+00
. 948E+00
. B53E+-00
.763E+00
. 677E+00
-595E+00
.517E+00
.443E+QO
. 373E+00
.306E+00
.242E+00
. 181E+00
. 124E+00
-069E+00
. 017E+00
. 673E-01
.2Q1E-01
-753E-Q1
-326E-01
-920E-01
D-15
-------
Table D-4. Northern Parcel Benzene Emisson Rate from Year 1968 to 2203 (continued).
A Case Study
Year
Refuse In Place (Mg)
(Mg/yr)
[Cubic m/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2035
2040
2041
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
20S5
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2080
2081
2082
2083
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
i.
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
917E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
2.
2,
2.
2.
2.
1.
1.
1,
1.
1.
1,
1.
1.
1,
1.
1.
1.
1,
9,
9.
9.
8.
8.
7.
7.
7.
6.
6.
6.
5.
5,
5,
4.
4.
4.
4.
4,
3.
3.
3.
3.
3.
2.
2.
2.
2.
2,
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
9.
8.
8.
7 ,
7.
448E-03
328E-03
215E-03
107E-03
004E-03
906E-03
813E-03
725E-03
641E-03
561E-03
485E-03
412E-03
343E-03
27SE-03
216E-03
156E-03
100E-03
046E-03
952E-04
467E-04
Q05E-04
566E-04
148E-04
751E-04
373E-04
013E-04
671E-04
346E-04
036E-04
742E-04
462E-04
195E-04
942E-04
701E-04
472E-04
254E-04
046E-04
S49E-04
661E-04
4S3E-04
313E-04
151E-04
997E-04
651E-04
712E-04
580E-04
454E-04
334E-04
221E-04
112E-04
009E-04
911E-04
818E-04
729E-04
645E-04
565E-04
489E-04
416E-04
347E-04
281E-04
219E-04
159E-04
103E-04
049E-04
978E-05
491E-05
028E-05
5S8E-05
169E-05
771E-05
392E-05
7
7
6
. 533E-01
.166E-01
.S17E-01
6.484E-01
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
3
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
.168E-01
.867E-01
.581E-01
-309E-01
. 050E-01
-304E-01
-569E-01
.346E-01
. 134E-01
. 933E-01
. 741E-01
.559E-01
-385E-01
.220E-01
. 063E-01
. 913E-01
.771E-01
. 636E-01
-508E-01
.385E-01
.269E-01
.158E-01
. 053E-01
. 953E-01
-858E-01
.767E-01
. 681E-01
.599S-01
.521E-01
. 447E-01
-376E-01
. 309E-01
-245E-01
-185E-01
.127E-01
. 072E-01
-02QE-01
. 898E-02
.22SE-02
.77SE-02
-347E-02
. 940E-02
.553E-02
.135E-02
-834E-02
. 501E-02
-184E-02
.S32E-02
-595E-02
.322E-02
.063E-02
. 316E-02
-581E-02
.358E-02
-145E-02
. 943E-02
-751E-02
. 568E-02
. 394E-02
-228E-02
-071E-02
. 921E-02
.779E-02
.643E-02
-514E-02
-392E-02
-275E-02
D-16
-------
Rose Hill, Rl
Table D-4. Northern Parcel Benzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2034
2085
20B6
2087
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2146
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
7.
S.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
031E-05
688E-05
3S2E-05
052E-Q5
757E-05
476E-05
209E-05
955E-05
713E-05
4S3E-05
265E-05
057E-05
859E-05
671E-05
492E-05
321E-05
159E-05
005E-05
859E-05
719E-05
587E-05
460E-05
340E-05
226E-05
11SE-05
014E-05
916E-05
823E-05
734E-05
649E-05
569E-05
492E-05
42QE-05
35QE-05
284E-05
222E-05
162E-05
106E-05
052E-05
OOOE-05
9.516E-06
9.
8.
8.
7,
7.
7.
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
Q52E-06
610E-06
190E-OS
791E-06
411E-06
049E-OS
706E-06
379E-06
067E-06
772E-06
490E-06
222E-06
9S8E-OS
725E-06
495E-OS
276E-06
067E-06
869E-06
680E-06
501E-06
330E-06
167E-06
013E-06
866E-06
726E-OS
593E-06
467E-OS
347E-06
232E-06
123E-06
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
a.
3,
7.
7 .
7.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
9.
9,
8.
8.
7.
7 .
7.
6.
6.
164E-02
058E-02
958E-02
863E-02
772E-02
685E-02
603E-02
525E-02
451E-02
330E-02
313E-02
248E-02
188E-02
130E-02
075E-02
022E-02
723E-03
249E-03
798E-03
369E-03
961E-03
572E-03
203E-03
S52E-03
518E-03
200E-03
397E-03
610E-03
336E-03
076E-03
828E-03
593E-03
369E-03
156E-03
953E-03
760E-03
577E-03
403E-03
237E-03
079E-03
929E-03
786E-03
650E-03
521E-03
398E-03
281E-03
170E-03
064E-03
963E-03
867E-03
776E-03
690E-03
607E-03
529E-03
454E-03
383E-03
316E-03
252E-03
191E-03
133E-03
077E-03
025E-03
748E-04
273E-04
821E-04
391E-04
9B1E-04
592E-04
222E-04
87QE-04
535E-04
D-17
-------
A Case Study
Table D-4. Northern Parcel Benzene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
[Cubic m/yr)
2155
2156
2157
2156
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2131
21B2
2183
2184
2185
2186
2187
213B
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
I.
1,
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+05
977E+05
977E+05
977E+Q5
977Ef05
977E+QS
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-f-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7.
7.
7.
6.
6.
6.
5.
5.
5.
4.
4.
4,
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
020E-06
92 IE- 06
827E-06
738E-06
654E-OS
S73E-06
496E-06
423E-06
354E-06
288E-06
225E-06
165E-06
108E-06
054E-06
003E-06
540E-07
075E-07
632E-07
211E-07
811E-07
430E-07
068E-07
723E-07
395E-07
083E-07
786E-07
504E-07
236E-07
980E-07
738E-07
50TE-07
287E-07
078E-07
879E-07
690E-07
510E-07
339E-07
176E-07
021E-07
873E-07
733E-07
6QOE-Q7
473E-07
353E-07
238E-07
129E-07
025E-07
926E-07
832E-07
6.
B.
5.
5.
5.
4.
4.
4,
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
9.
9.
8.
8.
8.
7,
7.
6.
6.
6.
5.
5.
216E-04
913E-04
624E-04
350E-04
089E-04
841E-04
605E-04
380E-04
167E-04
963E-04
770E-04
586E-Q4
411E-04
24SE-04
Q37E-04
936E-04
793E-04
6S7E-04
527E-04
404E-Q4
237E-04
175E-04
069E-04
968E-04
872E-04
781E-04
694E-04
611E-04
533E-04
458E-04
387E-04
319E-04
255E-04
194E-04
136E-04
030E-04
027E-04
774E-05
297E-05
S44E-05
412E-05
002E-05
612E-05
241E-Q5
887E-05
551E-05
232E-05
928E-05
639E-05
D-18
-------
Rose Hill, Rl
Table D-5. Northern Parcel Chlorobenzene Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\NORTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 1 volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : Chlorobenzene (HAP/VOC)
Molecular wt - 112.56 Concentration - 0-220000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Year
Refuse In Place {Mg)
Chlorobenzene (HAP/VOC) Emission Rate
(Mg/yr) (Cubic tn/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 31SE+04
. 636E+04
.954E+04
.272E+Q4
, 590E+04
. 908E+04
.226E+04
. 054E+05
. 186E+05
.318E+Q5
.450E+05
.5S2E+05
. 713E+05
.845E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
-977E+05
2.
4.
5,
7.
9.
1.
1.
1.
1.
1.
1.
1.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
e.
7 .
7.
7 .
6.
6.
6.
5.
5.
5.
4.
OSOE-04
020E-04
885E-04
658E-04
345E-04
095E-03
248E-03
393E-03
531E-03
662E-03
787E-03
906E-03
019E-03
127E-03
229E-03
120E-03
017E-03
919E-03
825E-03
736E-03
651E-03
571E-03
494E-03
421E-03
352E-03
286E-03
223E-03
1S4E-03
107E-03
053E-03
002E-03
527E-04
063E-04
621E-04
200E-04
800E-04
420E-04
058E-04
714E-04
386E-04
075E-04
779E-04
497E-04
229E-04
974E-04
4
8
1
1
1
2
2
2
3
3
3
4
4
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
. 401E-02
.537E-02
-257E-01
. 636E-01
, 996E-01
.339E-01
. 665E-01
. 975E-01
-270E-01
.551E-01
-818E-01
. 071E-01
.313E-01
. 543E-01
.761E-01
.529E-01
.308E-01
.098E-01
, 898E-01
. 708E-01
-527E-01
.355E-01
-192E-01
. 036E-01
.888E-01
. 747E-01
-613E-01
. 486E-01
-364E-01
.249E-01
, 139E-01
.035E-01
. 936E-01
. S41E-01
. 752E-01
. 666E-01
. 5B5E-01
.508E-01
.434E-01
.364E-01
.298E-01
.234E-01
-174E-01
, 117E-01
. 062E-01
D-19
-------
A Case Study
Table D-5. Northern Parcel Chlorobenzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
4.731E-04
4.SOOE-04
4.231E-04
4.072E-04
3.874E-04
3-635E-04
3.505E-04
3.334E-04
3.171E-04
3.017E-04
2.870E-04
2.730E-04
2.597E-04
2.470E-04
2.349E-04
2.235E-04
2.126E-04
2.022E-04
1.924E-04
1.830E-04
1.741E-04
1.656E-04
1.575E-04
1.498E-04
1.425E-04
1.356E-04
1.299E-04
1.227E-04
1.167E-04
1.110E-04
1.056E-04
1.004E-04
9.552E-05
9.036E-05
8.643E-05
8.222E-05
7.821E-05
7.439E-05
7.076E-05
6.731E-05
6.403E-05
6.091E-05
5.794E-05
5.511E-05
5.242E-05
4.987E-05
4-743E-05
4.512E-05
4.292E-05
4.033E-05
3.884E-05
3.694E-05
3-514E-05
3.343E-05
3.180E-05
3.025E-05
2.87TE-05
2.737E-05
2.603E-05
2.476E-05
2-356E-05
2.241E-05
2-131E-Q5
2.02TE-05
1.929E-05
1.834E-05
1.745E-05
1.660E-05
1.579E-05
1.502E-05
1.429E-05
1.011E-01
9.613E-02
9.144E-02
8.698E-02
8.274E-02
7.870E-02
7.4S7E-02
7.121E-02
6.774E-02
6.444E-02
6.129E-02
5-831E-02
5.546E-02
5.276E-02
5.01SE-02
4.774E-02
4.541E-02
4.319E-02
4.109E-02
3.908E-02
3.71GE-02
3.536E-02
3.364E-02
3.2QOE-02
3.044E-02
2.895E-02
2.754E-02
2.620E-02
2.492E-02
2.371E-02
2.255E-02
2.145E-02
2.040E-02
1.941E-Q2
1.846E-02
1.756E-02
1.67QE-02
1.589E-02
1.512E-02
1.438E-02
1.368E-02
1.301E-02
1.238E-02
1.177E-02
1.120E-02
1.065E-02
1.013E-02
9.636E-03
9.168E-03
8.721E-03
8.295E-03
7.891E-03
7.506E-03
7.140E-03
6.792E-03
6.460E-03
6.145E-03
5.846E-03
5.561E-03
5.289E-03
5.031E-03
4.736E-Q3
4.553E-03
4.331E-03
4.119E-03
3.918E-03
3.727E-03
3.546E-03
3.373E-03
3.208E-03
3.052E-03
D-20
-------
Rose Hill, Rl
Table D-5. Northern Parcel Chlorobenzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2084
20BS
20B6
2037
2038
20B9
2090
2091
2092
2093
2094
2095
209S
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-1-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
1.
1.
1.
1.
1.
1.
1.
9,
9.
8.
8.
7.
7.
7,
e.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
9.
9.
8.
8,
7 .
7.
7.
6.
6.
6.
5,
5.
5.
5.
4.
4-
4.
4.
359E-05
293E-05
230E-05
170E-05
113E-05
058E-OS
007E-05
577E-06
11GE-06
6S6E-06
243E-06
841E-06
459E-06
095E-06
749E-06
420E-06
107E-06
S09E-06
525E-06
256E-06
OOOE-06
756E-06
524E-06
303E-OS
093E-06
894E-06
704E-06
523E-06
351E-06
138E-06
032E-06
885E-06
744E-06
610E-06
483E-06
362E-06
246E-06
137E-06
033E-06
934E-06
839E-06
750E-06
664E-06
533E-06
506E-06
432E-06
3 63 E- 06
296E-06
233E-06
173E-06
116E-06
061E-06
OOSE-06
602E-07
133E-07
688E-07
264E-07
861E-07
478E-07
113E-07
766E-07
436E-07
122E-07
824E-07
540E-07
270E-07
013E-07
7SSE-07
536E-07
314E-07
104E-07
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
.9Q3E-03
-761E-03
. 627E-03
-499E-03
.377E-03
-261E-Q3
. 150E-03
-046E-03
. 946E-03
-351E-03
.761E-03
. 675E-03
.593E-03
-51SE-03
. 442E-03
.371E-03
-304E-03
-241E-03
.180E-03
-123E-03
. 068E-03
. 016E-03
. 663E-04
-192E-04
.743E-Q4
-317E-Q4
. 911E-04
. 525E-04
-158E-04
.309E-04
.477E-04
.161E-04
. 961E-04
.575E-04
.3Q3E-Q4
. 044E-04
. 798E-04
-564E-04
.342E-04
. 130E-04
-929E-Q4
.737E-04
-555E-04
.331E-04
-216E-04
.060E-04
. 910E-04
. 768E-04
. 633E-04
.505E-04
-333E-04
.267E-04
-156E-Q4
. 051E-04
. 951E-04
.356E-04
.765E-04
.679E-04
-597E-Q4
.519E-04
. 445E-04
.375E-04
-308E-04
.244E-04
-183E-04
.126E-04
-071E-04
. 01GE-Q4
-6B8E-05
-215E-05
.766E-05
D-21
-------
A Case Study
Table D-5. Northern Parcel Chlorobenzene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
[Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2163
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
21B1
2132
2183
21B4
2185
2136
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+-05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+QS
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-1-05
1.977E+05
1.977E-<-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
3.9Q4E-07
3.713E-07
3.532E-07
3.360E-07
3.196E-07
3.040E-07
2.892E-07
2.751E-07
2.617E-07
2.439E-07
2.368E-07
2.252E-07
2.142E-07
2.D38E-07
1.939E-07
1.844E-07
1.754E-07
1.669E-07
1.587E-07
1.S10E-07
1.436E-07
1.366E-07
1.299E-07
1.236E-07
1.176E-07
1.118E-07
1.064E-07
1.012E-07
9. 627 E- 08
9.157E-08
8.710E-08
8.236E-OS
7.882E-08
7.497E-08
7.132E-08
6.734E-08
6.453E-08
6.138E-06
5.839E-08
5.554E-08
5.283E-08
5.026E-OS
4.180E-08
4.547E-06
4.325E-08
4.115E-08
3.914E-08
3.723E-08
3.541E-08
8.338E-05
7.932E-05
7.545E-05
7.177E-05
6.827E-05
6.494E-05
6.177E-05
5.S76E-05
5.539E-05
5.317E-05
5.057E-05
4.811E-05
4.576E-05
4.353E-05
4.141E-05
3.939E-05
3.747E-05
3.5€4E~05
3.390E-05
3.22SE-05
3.068E-05
2.918E-05
2.776E-05
2.640E-05
2.511E-05
2.389E-05
2.272E-05
2.162E-05
2.056E-05
1.956E-05
1.861E-05
1.770E-05
1.S83E-05
1.601E-05
1.523E-05
1.449E-05
1.378E-05
1.311E-05
1.247E-05
1.136E-05
1.128E-05
1.073E-05
1.Q21E-05
9.713E-06
9.239E-06
8.739E-06
8.360E-06
7.952E-06
7.564E-06
D-22
-------
Rose Hill, Rl
Table D-6. Northern Parcel Chloroethane Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\NORTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 1 volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : Chloroethane (HAP/VOC)
Molecular wt - 64.52 Concentration - 2.960000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Year
Refuse In Place {Mg)
Chloroethane (HAP/VOC) Emission Rate
(Mg/yr) (Cubic tti/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 31SE+04
. 636E+04
.954E+04
.272E+Q4
, 590E+04
. 908E+04
.226E+04
. 054E+05
. 186E+05
.318E+05
.450E+05
.5S2E+05
. 713E+05
.845E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
.977E+05
1.
3.
4.
5.
7 .
8.
9.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
e.
8.
7 .
7 .
6.
6.
6.
e.
5.
5.
5.
4.
4.
4.
4.
4.
3.
589E-03
101E-03
538E-03
9Q6E-03
207E-03
445E-03
622E-03
074E-02
181E-02
232E-02
378E-02
470E-02
557E-02
640E-02
719E-02
635E-02
556E-02
480E-02
408E-02
339E-02
274E-02
211E-Q2
152E-02
096E-02
043E-02
918E-03
435E-03
975E-03
S37E-03
121E-03
725E-03
348E-03
989E-03
649E-03
324E-03
016E-03
723E-03
443E-03
178E-03
925 E- 03
685E-03
457E-03
239E-03
033E-03
836E-03
5
1
1
2
2
3
3
4
4
4
5
5
5
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
. 921E-01
. 155E+00
. 691E+00
.201E+00
, 686E+00
.147E+00
.585E+00
. 003E+00
-400E+00
.777E+00
-136E+00
.478E+00
.803E+00
. 112E+00
.406E+00
. 094E+00
.796E+00
.514E+00
-245E+00
. 989E+00
-746E+00
.514E+00
-294E+00
. 085E+00
. 886E+00
. 696E+00
-516E+00
.344E+00
-181E+00
. 026E+-00
, 878E+00
.738E+00
. 605E+00
. 478E+00
-357E+00
.242E+00
. 132E+00
. 028E+00
.929E+00
. S35E+00
.746E+00
. 661E+00
-580E+00
, 503E+00
. 429E+00
D-23
-------
A Case Study
Table D-6. Northern Parcel Chloroethane Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2033
1.977E+Q5
1.977E+05
1.977E+05
1 .977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1-977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E-h05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
3.649E-03
3.471E-03
3.302E-03
3.141E-03
2.937E-03
2.842E-03
2.703E-03
2.571E-03
2.446E-03
2.327E-03
2.213E-03
2.105E-03
2.003E-03
1.905E-03
1.812E-03
1.724E-03
1.640E-03
1.560E-03
1.484E-03
1.411E-03
1.342E-03
1.277E-03
1.215E-03
1.155E-03
1.099E-03
1.045E-03
9.944E-04
9.459E-04
8.998E-04
8.559E-04
8.142E-04
7.745E-04
7.367E-04
7.008E-04
6.666E-04
6.341E-04
6.031E-04
5.737E-04
5.458E-04
5.191E-04
4.938E-04
4.697E-04
4.468E-04
4.250E-04
4.043E-04
3.846E-04
3.658E-04
3.480E-04
3.31DE-04
3.149E-04
2.995E-04
2.849E-04
2.710E-04
2.57SE-04
2.452E-Q4
2.333E-04
2.219E-04
2.111E-04
2.008E-04
1.910E-04
1.817E-04
1.72BE-04
1.644E-04
1.564E-04
1.487E-04
1.415E-04
1.346E-04
1.230E-04
1.218E-04
1.158E-04
1.102E-04
1.360E+00
1.293E+00
1.230E+00
1.170E+00
1.113E+00
1.059E+00
1.007E+00
9.582E-01
9.114E-01
8.670E-01
8.247E-01
7.845E-01
7.462E-01
7.098E-01
6.752E-01
6.423E-01
6.109E-01
5.S12E-01
5.528E-01
5.258E-01
5.002E-01
4.758E-01
4.526E-01
4.305E-01
4.095E-01
3.896E-01
3.706E-01
3.525E-01
3.353E-01
3.189E-01
3.034E-01
2.886E-01
2.745E-01
2.611E-01
2.4B4E-01
2.363E-01
2.248E-01
2.138E-01
2.034E-01
1.934E-01
1.840E-01
1.750E-01
1.665E-01
1.5B4E-01
1.507E-01
1.433E-01
1.363E-01
1.297E-01
1.233E-01
1.173E-01
1.116E-01
1.062E-01
1.010E-01
9.S06E-02
9-138E-02
8 . 692E-02
8.268E-02
7.365E-02
7.481E-02
7.117E-02
6-770E-02
6.439E-02
6.125E-02
5.827E-02
5.542E-02
5.272E-02
5.015E-02
4.770E-02
4-538E-Q2
4.316E-02
4.106E-02
D-24
-------
Rose Hill, Rl
Table D-6. Northern Parcel Chloroethane Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
[Cubic m/yr)
2084
20BS
20B6
2037
2038
2089
2090
2091
2092
2093
2094
2095
209S
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+QS
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-H35
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
I.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.G48E-04
9.970E-05
9.434E-05
9.021E-Q5
8.531E-05
8.163E-05
7.765E-05
7.336E-05
7.026E-05
6.633E-05
6.357E-05
6.047E-05
5.752E-05
5.472E-05
5. 2 05 E- 05
4.951E-05
4.709E-05
4.430E-05
4.2S1E-05
4.053E-05
3.856E-05
3.668E-05
3.489E-05
3.319E-05
3.157E-05
3.003E-05
2.856E-05
2.717E-05
2.585E-05
2.459E-05
2.339E-05
2.225E-05
2.116E-05
2.013E-05
1.915E-05
1.821E-05
1.733E-05
1.648E-05
1.568E-05
1.491E-05
1.418E-05
1.349E-05
1-283E-05
1.221E-05
1.161E-05
1.105E-05
1.051E-Q5
9.99SE-06
9.508E-06
9.045E-06
8.603E-06
8.134E-06
7.735E-06
7.405E-06
7.044E-06
6.700E-06
6.374E-06
6.063E-06
5.767E-06
5.436E-06
5.218E-06
4.964E-06
4.722E-06
4.491E-06
4.272E-06
4.0S4E-06
3.866E-06
3.677E-06
3.498E-06
3.327E-06
3.165E-06
3.9Q6E-02
3.715E-02
3.534E-02
3.3S2E-02
3.198E-02
3.042E-02
2.B93E-02
2.752E-02
2.618E-02
2.490E-02
2.369E-02
2.253E-02
2.143E-02
2.039E-02
1.939E-02
1.845E-02
1.755E-02
1.669E-02
1.538E-02
1.510E-02
1.437E-02
1.367E-02
1.300E-02
1.237E-02
1.176E-02
1.119E-02
1.064E-02
1.013E-02
9.631E-03
9.162E-03
8.715E-03
8.290E-03
7.885E-03
7.501E-03
7.135E-03
6.737E-03
6.456E-03
6.141E-03
5.842E-03
5.557E-03
5.286E-03
5.028E-03
4.783E-03
4.549E-03
4.328E-03
4.117E-03
3.916E-03
3.725E-03
3.543E-03
3.370E-03
3.206E-03
3.050E-03
2.901E-03
2.759E-03
2.625E-03
2.497E-03
2.375E-03
2.259E-03
2.149E-03
2.044E-03
1.945E-03
1.B50E-03
1.759E-03
1.674E-03
1.592E-03
1.514E-03
1.441E-03
1.370E-03
1.303E-03
1.240E-03
1.179E-03
D-25
-------
A Case Study
Table D-6. Northern Parcel Chloroethane Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E-<-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
3.011E-06
2.864E-06
2.724E-06
2.591E-06
2.465E-06
2-345E-06
2.230E-06
2.122E-06
2.01BE-06
1.920E-06
1.826E-06
1.737E-06
1.652E-06
1.S72E-06
1.495E-06
1.422E-06
1.353E-06
1.237E-06
1.224E-06
1.164E-06
1.10SE-06
1.054E-06
1.002E-06
9.533E-07
9.068E-07
8.626E-07
8.205E-07
7.805E-07
7.424E-07
7.062E-07
6.718E-07
6.390E-07
6.078E-07
5.732E-07
5.500E-07
5.232E-07
4.977E-07
4.734E-07
4.503E-07
4.2S3E-07
4.074E-07
3.876E-07
3.687E-07
3.507E-07
3.336E-07
3.173E-07
3-018E-07
2.871E-07
2.731E-07
1.122E-03
1.067E-03
1.015E-03
9.656E-04
9.185E-04
8.737E-04
S.311E-04
7.906E-04
7.520E-04
7.153E-04
6.805E-04
6.473E-04
6.157E-04
5.857E-04
5.571E-04
5.299E-04
5.041E-04
4.795E-04
4.561E-04
4.339E-04
4.127E-04
3.926E-04
3.734E-04
3.552E-04
3.379E-04
3.214E-04
3.058E-04
2.908E-04
2.767E-04
2.632E-04
2.503E-04
2.381E-04
2.265E-04
2.155E-04
2.050E-04
1.950E-04
1.854E-04
1.764E-04
1.678E-04
1.596E-04
1.518E-04
1.444E-04
1.374E-04
1.307E-04
1.243E-04
1.182E-04
1.125E-04
1.070E-04
1.018E-04
D-26
-------
Rose Hill, Rl
Table D-7. Northern Parcel Dichlorobenzene Emisson Rate from Year 1968 to 2203.
Source: H:\3000V030177~1.000\030177~1.002\ROSEHI~1\NORTHERN.PRM
Model Parameters
Lo s 170.00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 $ volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : Dichlorobenzene [VOC/HAP for 1,4 isomer)
Molecular wt - 147.00 Concentration - 0.100000 ppmV
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Dichlorobenzene (VOC/HAP for 1,4 isomer) Emission Ra
Year Refuse In Place (Mg) (Mg/yr) (Cubic m/yr)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1931
1982
1933
1984
19S5
1936
1987
1988
19B9
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
I
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
I
. 318E+04
. 636E+Q4
. 954E+04
.272E+04
.590E+04
. 9Q8E+04
.226E+04
. 054E+05
. 186E+05
. 318E+05
.450E+05
.582E+05
. 713E+05
.B45E+05
. 977E+Q5
. 977E+Q5
.977E+05
. 977E+Q5
.977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
, 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
-977E+05
-977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
1.
2.
3.
4.
5.
6.
7.
S.
9.
9.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
8.
7 .
7.
S.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
223E-04
387E-04
493E-04
546E-04
547E-04
500E-04
406E-04
268E-04
088E-04
8S8E-04
061E-03
132E-03
199E-03
263E-03
323E-03
259E-03
197E-03
139E-03
083E-03
031E-03
803E-04
325E-04
870E-04
437E-04
026E-04
634E-04
262E-04
90BE-04
571E-04
251E-04
946E-04
656E-04
380E-04
118E-04
868E-04
631E-04
405E-04
190E-04
986E-04
791E-04
606E-04
430E-04
263E-04
104E-04
953E-04
2
3
5
7
9
1
1
1
1
1
1
1
1
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
5
4
. OOOE-02
.903E-02
.713E-02
.435E-02
. 073E-02
. 063E-01
.211E-01
.352E-01
-486E-Q1
. 614E-01
.735E-01
-851E-01
. 960E-01
. 065E-01
. 164E-01
.Q59E-01
. 958E-01
.863E-01
-772E-01
. 686E-01
. 603E-01
.525E-01
-451E-01
. 380E-01
-313E-01
.249E-01
. 188E-01
. 130E-01
-075E-01
.022E-01
-725E-02
.250E-02
.799E-Q2
. 370E-02
. 962E-02
.573E-02
.204E-02
-853E-02
-519E-02
.201E-02
-898E-02
. 611E-02
-337E-Q2
-077E-02
-829E-02
D-27
-------
A Case Study
Table D-7. Northern Parcel Dichlorobenzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
2.3Q9E-04
2.672E-04
2.541E-04
2.417E-04
2.299E-04
2-187E-04
2.031E-04
1.979E-04
1.883E-04
1.791E-04
1.703E-04
1.620E-04
1.541E-04
1.466E-04
1.395E-04
1.327E-04
1.262E-04
1.200E-04
1.142E-04
1.086E-04
1.Q33E-04
9. 828 E- 05
9.349E-05
8.893E-05
8.459E-05
8.047E-05
7.654E-05
7.281E-05
6.926E-05
6.588E-05
6.267E-05
5.961E-05
5.670E-05
5.394E-05
5-131E-05
4.881E-05
4.643E-05
4.416E-05
4.201E-05
3.996E-05
3.801E-05
3.616E-05
3.439E-05
3.272E-05
3.112E-05
2.960E-05
2-816E-05
2.679E-05
2.548E-05
2.424E-05
2.305E-05
2.193E-05
2-OB6E-05
1.934E-05
1.888E-05
1.795E-05
1.108E-05
1.625E-05
1.545E-05
1.470E-05
1.398E-05
1.330E-05
1-265E-05
1.204E-05
1.145E-05
1.039E-05
1.036E-05
9.854E-06
9.373E-Q6
8.916E-06
8.431E-06
4.594E-02
4.370E-02
4.156E-02
3.954E-02
3.761E-02
3.577E-02
3.403E-02
3.237E-02
3.079E-02
2.929E-02
2.736E-02
2-650E-02
2.521E-02
2.398E-02
2.281E-02
2.170E-02
2.064E-02
1.963E-02
1.368E-02
1.777E-02
1.690E-02
1.607E-02
1.529E-02
1.454E-02
1.334E-02
1.316E-02
1.252E-02
1.191E-02
1.133E-02
1.078E-02
1.025E-02
9.750E-03
9.274E-03
6.822E-Q3
8.392E-03
7.982E-03
7.593E-03
7.223E-03
6.871E-03
6.535E-03
6.217E-03
5.914E-03
5.625E-03
5.351E-03
5.090E-03
4.342E-03
4.605E-03
4.331E-03
4.167E-03
3.964E-03
3.771E-03
3.537E-03
3.412E-03
3.245E-03
3.087E-03
2.937E-03
2.793E-03
2.657E-03
2.528E-03
2.404E-03
2.287E-03
2.175E-Q3
2.069E-03
1.968E-03
1.872E-03
1.731E-03
1.694E-03
1.612E-03
1.533E-03
1.458E-03
1.387E-03
D-28
-------
Rose Hill, Rl
Table D-7. Northern Parcel Dichlorobenzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2084
2035
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2095
209"?
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
210.8
2109
2110
2111
2112
2113
2114
2115
2116
2117
2116
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+OS
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+-05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-»-05
977E+05
977E-1-05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
8.
7.
7.
6.
6.
6,
5.
5.
5,
5.
4.
4.
4.
4.
4.
3.
3.
3,
3.
3,
2.
2.
2.
2.
2.
2.
2.
2,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
8.
7.
7.
6.
6-
6.
5.
5.
5.
5.
4,
4.
4.
4.
4.
3-
3.
3.
3.
3.
2.
2.
2.
2.
2.
068E-06
674E-06
300E-06
944E-06
605E-06
283E-06
977E-06
685E-06
408E-06
144E-06
893E-06
655E-06
428E-06
212E-06
006E-06
811E-06
625 E- 06
448E-06
290E-06
120E-06
968E-06
823E-06
685E-06
554E-06
430E-06
311E-06
199E-06
091E-06
939E-06
892E-06
800E-06
712E-06
629E-06
549E-06
474E-06
402E-06
334E-06
269E-06
207E-06
148E-06
092E-OS
039E-06
879E-07
397E-07
939E-07
503E-07
038E-07
694E-07
319E-07
962E-07
622E-07
299E-07
992E-07
700E-07
422E-07
157E-07
906E-07
667E-07
439E-07
223E-07
017E-07
821E-07
634E-07
457E-07
288E-07
12GE-07
976E-07
830E-07
692E-Q7
561E-07
436E-07
1
1
1
1
1
1
9
9
8
a
8
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
3
8
8
7
7
6
6
6
5
5
5
5
4
4
4
4
3
-319E-03
.255E-03
.194E-03
.136E-03
. 080E-03
. 028E-03
-775E-04
.298E-04
.845E-04
. 413E-04
.003E-04
-613E-04
.241E-04
.888E-04
-552E-04
-233E-04
, 929E-04
. 640E-04
.365E-04
.103E-04
.854E-04
. 617E-04
-392E-04
. 176E-04
.974E-04
-780E-04
.596E-04
. 421E-Q4
•254E-04
.095E-04
. 944E-04
. 801E-04
. 664E-04
-534E-04
. 410E-04
.293E-04
-181E-04
.075E-04
. 974E-04
. 377E-04
. 786E-04
.699E-04
-616E-04
.537E-04
-462E-04
. 391E-04
-323E-04
-258E-04
. 197E-04
. 139E-04
-083E-04
. 030E-04
.80QE-05
•322E-05
. 36BE-05
-435E-05
.024E-OS
. 632E-05
-260E-OS
. 9Q6E-05
.569E-05
-249E-05
. 944E-05
.654E-05
-379E-05
. 116E-05
.867E-05
. 629E-05
.404E-05
-189E-05
. 934E-05
D-29
-------
A Case Study
Table D-7. Northern Parcel Dichlorobenzene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E-<-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
2.317E-07
2.204E-07
2.097E-07
1.995E-07
1.897E-07
1.805E-07
1.717E-07
1.633E-07
1.553E-07
1.478E-07
1.406E-07
1.337E-07
1.272E-07
1.210E-07
1.151E-07
1.095E-07
1.041E-07
9.905E-08
9.422E-08
8.962E-08
B.525E-08
8.109E-08
7.714E-08
7.338E-08
6.980E-08
6.639E-08
6.316E-08
6.008E-08
5.T15E-08
5.436E-08
5.171E-08
4.919E-08
4.679E-08
4.450E-03
4.233E-08
4.027E-08
3.831E-08
3.644E-OS
3.466E-08
3.297E-08
3.136E-08
2.983E-08
2.838E-08
2.699E-08
2.568E-08
2.442E-08
2-323E-08
2.210E-OB
2.102E-08
3.790E-05
3.605E-05
3.429E-05
3.262E-05
3.103E-05
2.952E-05
2.30GE-05
2.671E-05
2.541E-05
2.417E-05
2.299E-05
2.187E-05
2.030E-05
1.979E-05
1.BB2E-05
1.790E-05
1.703E-05
1.620E-05
1.541E-05
1.466E-05
1.394E-05
1.326E-05
1.262E-OS
1.2QOE-05
1.142E-05
1.Q86E-05
1.033E-05
9.826E-06
9.346E-06
8.391E-06
8.457E-06
8.045E-06
7.652E-06
7.279E-06
6.924E-06
6.5B6E-06
6.265E-06
5.960E-06
5.669E-06
5.392E-06
5.129E-06
4.879E-06
4.641E-06
4.415E-06
4.200E-06
3.995E-06
3.800E-06
3.615E-06
3.438E-06
D-30
-------
Rose Hill, Rl
Table D-8. Northern Parcel Toluene Emisson Rate from Year 1968 to 2203.
Source: H: \3000\030177~1. OOOSQ30177~1. 002\.ROS£HI~1\NORTHERN. PRM
Model Parameters
Lo s 170.00 wA3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 % volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : Toluene (HAP/VOC)
Molecular Wt - 92.14 Concentration - 1.120000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Year
Refuse In Place {Mg)
Toluene (HAP/VOC) Emission Rate
CMg/yr) (Cubic ra/yr)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1931
1982
19S3
1984
1985
1986
1987
1988
19B9
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 313E+04
. 636E+04
-954E+04
. 272E+Q4
.590E+04
. 90SE+04
.226E+04
. 054E+05
. 186E+Q5
.318E+05
-450E+05
-562E+05
. 713E+05
. 345E+05
-977E+05
. 977E+Q5
.977E+05
. 977E+Q5
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+Q5
. 977E+05
.977E+05
. 977E+-05
. 977E+05
•977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
-977E+-05
.977E+05
8.
1.
2.
3.
3.
4.
5.
5.
6.
6.
7 .
7.
8.
S.
9,
8.
8.
7.
7.
7 .
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
596E-04
675E-03
452E-03
191E-03
894E-03
563E-03
199E-03
8Q4E-03
380E-03
927E-03
448E-03
944E-03
415E-03
863E-03
289E-03
836E-03
405E-03
995E-03
606E-03
235E-03
882E-03
546E-03
227E-03
923E-03
634 E- 03
360E-03
098E-03
849E-03
613E-03
338E-03
174E-03
970E-03
777E-03
593E-03
417E-03
251E-03
092E-03
941E-03
798E-03
661E-03
532E-03
408E-03
291E-03
179E-03
073E-03
2
4
6
8
1
1
1
1
1
1
1
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
8
7
7
6
6
6
5
5
5
.241E-01
. 372E-01
-399E-01
.327E-01
.016E+00
. 191E+00
.357E+00
. 515E+00
.665E+00
. 808E+00
. 943E+00
-073E+00
.196E+00
.313E+00
.424E+00
. 306E+00
. 193E+00
. 036E+00
, 985E+00
.888E+00
. 796E+00
. 708E+00
-625E+00
. 546E+00
-470E+00
.398E+00
-330E+00
.265E+00
-204E+QO
.145E+00
-089E+00
.036E+00
-855E-01
.374E-01
. 917E-01
. 432E-01
-069E-01
-675E-01
.301E-01
. 945E-01
. 606E-01
.234E-01
. 977E-01
. 686E-01
.409E-01
D-31
-------
A Case Study
Table D-8. Northern Parcel Toluene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.972E-03
1.876E-03
1.784E-03
1.697E-03
1.614E-03
1.S36E-Q3
1.461E-03
1.389E-03
1.322E-03
1.257E-03
1.196E-03
1.138E-03
1.082E-03
1.029E-03
9.791E-04
9.313E-04
8.859E-04
8.427E-04
8.016E-04
7.625E-04
7.253E-04
6.9QOE-04
6.563E-04
6.243E-04
5.939E-04
5.649E-04
5.373E-04
5.111E-04
4.862E-04
4.625E-04
4.399E-04
4.185E-04
3.931E-04
3.787E-04
3.602E-04
3.426E-04
3.259E-04
3.100E-04
2.949E-04
2.805E-04
2.668E-04
2.538E-04
2.414E-04
2.297E-04
2.185E-04
2.078E-04
1-977E-04
1.830E-04
1-789E-04
1.701E-Q4
1.618E-04
1.540E-04
1-4S4E-04
1.393E-04
1.325E-04
1.260E-04
1.199E-04
1.140E-04
1.085E-04
1.032E-04
9.816E-05
9.338E-05
8-882E-05
8.449E-05
8.037E-05
7.645E-05
7.272E-05
S.917E-05
6.580E-05
6.259E-05
5.954E-05
5.145E-01
4.894E-01
4.655E-01
4.428E-01
4.212E-01
4.007E-01
3.311E-Q1
3.625E-01
3.449E-01
3.280E-01
3.120E-01
2-968E-01
2.324E-01
2.686E-01
2.555E-01
2.430E-01
2.312E-01
2.199E-01
2.092E-01
1.990E-01
1.393E-01
1.800E-01
1.713E-01
1.629E-01
1.550E-01
1.474E-01
1.402E-01
1.334E-01
1.269E-01
1.207E-01
1.148E-01
1.092E-01
1.039E-01
9.331E-02
9.399E-02
8.940E-02
8.504E-02
8.090E-02
7.695E-02
7.320E-02
6.963E-02
6.623E-02
6.300E-02
5.993E-02
5.701E-02
5.423E-02
5.158E-02
4.907E-02
4.667E-02
4.440E-02
4.223E-02
4.017E-02
3.821E-02
3.635E-02
3.458E-02
3.239E-02
3.129E-02
2.976E-02
2.831E-02
2.693E-02
2.561E-02
2.437E-Q2
2.318E-02
2.205E-02
2.Q97E-02
1.995E-02
1.898E-02
1.305E-02
1.717E-02
1.633E-02
1.554E-02
D-32
-------
Rose Hill, Rl
Table D-8. Northern Parcel Toluene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
20B4
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
5.
5.
5.
4,
4.
4.
4.
3,
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
9.
9.
8.
8.
8.
7.
7 .
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
664E-05
387E-OS
125E-05
875E-05
637 E- 05
411E-05
196E-05
991E-05
796E-Q5
611E-05
435E-05
268E-05
108E-05
95 7 E- 05
812E-05
675E-05
545E-05
421E-05
303E-05
190E-05
Q34E-05
932E-05
885E-05
793E-05
706E-05
623 E- 05
543E-05
468E-05
397E-05
328E-05
264E-05
202E-05
143E-05
088E-05
035E-05
842E-06
362E-06
905E-06
471E-06
058E-Q6
665E-06
291E-06
935 E- 06
597E-06
275E-06
969E-06
678E-06
401E-06
138E-06
887E-06
649E-06
422E-06
207E-06
001E-06
806E-06
62 IE- 06
444E-06
276E-06
116E-06
964E-06
820E-06
6B2E-06
551E-06
427E-06
309E-06
196E-06
089E-06
937E-06
890E-06
798E-06
710E-06
1
1
1
1
1
1
1
1
9
9
8
e
8
1
7
6
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
8
7
7
6
6
6
6
5
5
5
4
4
4
.478E-02
.4Q6E-Q2
.337E-02
.272E-02
.210E-02
-151E-02
. 095E-02
-041E-02
. 906E-03
.423E-03
. 963E-03
. 526E-03
.110E-03
-715E-03
.339E-03
.931E-03
-640E-03
-316E-03
. 008E-03
-715E-03
. 437E-03
.171E-03
, 919E-03
. 679E-03
.451E-03
.234E-03
. 028E-03
.331E-03
-644E-03
.467E-03
.297E-03
. 137E-03
. 934E-03
. B38E-03
-7QOE-03
.568E-03
. 443E-03
-324E-03
.210E-03
. 103E-03
.OOOE-03
. 902E-03
.810E-03
.721E-03
.637E-03
.558E-03
-482E-03
. 409E-03
-341E-Q3
.275E-03
-213E-03
. 154E-03
-098E-03
.044E-03
. 932E-04
.447E-04
, 987E-04
.548E-04
. 131E-04
. 735E-04
.358E-04
. 999E-04
. 657E-04
-333E-04
.024E-04
. 730E-04
.451E-04
. 1B5E-04
. 932E-04
. 691E-04
. 463E-04
D-33
-------
A Case Study
Table D-8. Northern Parcel Toluene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
[Cubic m/yr)
2155
2156
2157
2156
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2131
21B2
2183
2184
2185
2186
2187
213B
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
I.
1,
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+05
977E+05
977E+05
977E+Q5
977Ef05
977E+OS
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-f-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
1
1
1
1
1
1
1
1
1
1
9
9
8
8
e
7
7
6
6
.627E-06
.547E-06
.472E-06
-400E-06
.332E-OS
-26"7E-06
.2Q5E-06
-146E-06
.090E-06
-037E-06
.867E-07
-386E-07
. 928E-07
-493E-07
.G79E-07
.685E-07
-310E-07
-953E-07
. 614E-07
6.292E-07
5
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
. 985E-07
.693E-07
-415E-07
-151E-07
.900E-07
.661E-07
. 434E-07
.217E-07
-012E-07
.816E-07
-630E-07
-453E-07
.285E-07
.124E-07
-972E-07
.827E-07
-689E-07
-558E-07
.433E-07
.315E-07
.202E-07
.094E-07
-992E-07
.895E-07
-803E-07
.715E-07
-631E-07
.551E-07
-476E-07
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
9,
8.
8.
7.
7.
7.
6.
6.
6.
5.
5.
5,
4.
4.
4.
4.
4.
3.
245E-04
Q38E-04
341E-04
654E-04
476E-04
306E-04
145E-04
991E-04
846E-04
707E-04
575E-04
449E-Q4
330E-04
216E-04
108E-04
005E-04
907E-04
814E-04
726E-04
642E-04
562E-04
435E-04
413E-04
344E-04
279E-04
216E-04
157E-04
100E-04
047E-04
957E-OS
472E-05
010E-05
570E-05
152E-05
755E-05
377E-05
017E-05
675E-05
349E-05
040E-05
745E-05
465E-05
198E-05
945E-05
704E-05
474E-05
256E-05
048E-05
851E-05
D-34
-------
Rose Hill, Rl
Table D-9. Northern Parcel Trichloroethene Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\NORTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 1 volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : Trichloroethene (HAP/VOC)
Molecular wt - 131.36 Concentration - 0.060000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Year
Refuse In Place {Mg)
Triohloroethene (HAP/VOC) Emission Rate
(Mg/yr) (Cubic m/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 313E+04
. 636E+04
.954E+04
.272E+04
, 590E+04
. 908E+04
.226E+04
. 054E+05
. 186E+05
.318E+Q5
-450E+05
.5S2E+05
. 713E+05
.845E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
.977E+05
6.
1.
1,
2.
2,
3.
3.
4.
4.
5.
5.
6.
6.
6.
7.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
559E-05
230E-04
873E-04
438E-04
975E-04
486E-04
971E-04
434E-Q4
873E-04
292E-04
689E-04
068E-04
428E-04
770E-04
096E-04
750E-04
421E-04
107E-04
810E-04
526E-04
257E-04
OQQE-Q4
756E-04
524E-04
304E-04
094E-04
894E-04
704E-04
S24E-04
352E-04
188E-04
033E-04
885E-04
744E-04
610E-04
433E-04
362E-04
247E-04
137E-04
033E-04
934E-04
840E-04
750E-04
664E-04
583E-04
1
2
3
4
5
6
7
8
8
9
1
1
1
1
1
1
1
1
1
1
9
9
S
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
.200E-02
.342E-02
. 428E-02
. 461E-02
.444E-02
.379E-02
.268E-02
. 114E-02
. 918E-02
. 684E-02
. 041E-01
. 110E-01
.176E-01
.239E-01
.299E-01
.235E-01
.175E-01
.118E-01
-063E-01
. 011E-01
. 620E-02
. 151E-02
-704E-02
.280E-02
.876E-02
. 492E-02
-127E-02
. 779E-02
-448E-02
. 134E-02
, 835E-02
.550E-02
.279E-02
. 022E-02
. 777E-02
.544E-02
-322E-02
. 112E-02
.911E-02
. 720E-02
.539E-02
. 366E-02
-202E-02
, 046E-02
. 897E-02
D-35
-------
A Case Study
Table D-9. Northern Parcel Trichloroethene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.5Q6E-04
1.433E-04
1.363E-04
1.296E-04
1.233E-04
1-173E-04
1.116E-04
1.061E-04
1.010E-04
9.603E-05
9.135E-05
8.689E-05
8.266E-05
"7.862E-05
7.479E-05
7.114E-05
6.767E-05
6.437E-OS
6.123E-05
5.825E-05
5.541E-05
5.270E-05
5.013E-05
4.769E-05
4.536E-05
4.315E-05
4.105E-05
3.904E-05
3.T14E-05
3.533E-05
3.361E-05
3.197E-05
3.041E-05
2.892E-05
2.751E-05
2.617E-05
2.490E-05
2.368E-05
2.253E-05
2.143E-05
2.038E-05
1.939E-05
1.844E-05
1.754E-05
1.663E-05
1.597E-05
1-510E-05
1.436E-05
1.366E-05
1.300E-05
1.236E-05
1.176E-05
1-119E-05
1.064E-05
1.012E-05
9.628E-Q6
9.158E-06
8.712E-06
8.287E-06
7.8S3E-06
7.498E-06
7.133E-06
6-785E-06
6.454E-06
6.139E-06
5.840E-06
5.S55E-06
5.234E-06
5.026E-06
4.781E-06
4.548E-06
2.756E-02
2.622E-02
2.494E-02
2.372E-02
2.257E-02
2.146E-02
2.042E-02
1.942E-02
1.847E-02
1.757E-02
1.672E-02
1.590E-02
1.513E-02
1.439E-02
1.369E-02
1.302E-02
1.238E-02
1-178E-02
1.121E-02
1.066E-02
1.014E-02
9.645E-03
9.174E-03
8.727E-03
8.301E-03
7.896E-03
7.511E-03
7.145E-03
6.797E-03
6.465E-03
6.150E-03
5.850E-03
5.565E-03
5.293E-Q3
5.035E-03
4.739E-03
4.556E-03
4.334E-03
4 . 122E-03
3.921E-03
3.730E-03
3.548E-03
3.375E-03
3.210E-03
3.054E-03
2.905E-03
2.763E-03
2.629E-03
2.500E-03
2.378E-03
2.262E-03
2.152E-03
2.047E-03
1.947E-03
1.852E-03
1.762E-03
1.676E-03
1.594E-03
1-517E-03
1.443E-03
1.372E-03
1.305E-03
1.242E-03
1.181E-03
1.123E-03
1.069E-03
1.017E-03
9.670E-04
9.198E-04
8.750E-04
8.323E-04
D-36
-------
Rose Hill, Rl
Table D-9. Northern Parcel Trichloroethene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
20B4
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
4.
4.
3.
3,
3.
3.
3.
3,
2.
2.
2.
Z.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9,
9.
8.
G.
7.
7 .
7 .
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
326E-06
115E-06
914E-06
724E-06
542E-06
369E-06
205E-06
049E-06
9QOE-Q6
758E-06
624 E- 06
496E-06
374E-06
258E-06
14BE-06
044E-06
944E-06
849E-06
759E-06
673E-06
592E-Q6
514E-06
440E-06
370E-06
303E-06
239E-06
179E-06
122E-06
067E-06
015E-06
653E-07
132E-07
734E-07
3Q8E-07
903E-07
518E-07
151E-07
802E-07
471E-07
15 5 E- 07
855E-07
569E-07
298E-07
039E-07
794E-07
560E-07
337E-07
126E-07
925 E- 07
733E-07
551E-07
378E-07
213E-07
056E-07
907E-07
7S6E-07
631E-07
502E-07
380E-07
2 64 E- 07
154E-07
Q49E-07
949E-07
854E-07
763E-07
677E-07
596E-07
51GE-07
444E-07
373E-07
306E-07
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
. 917E-04
.531E-Q4
. 164E-04
, 314E-Q4
.432E-04
. 166E-04
. 365E-04
-579E-04
.307E-04
.048E-04
. 802E-04
. 568E-04
.345E-04
-133E-04
. 931E-04
.740E-04
-557E-04
-384E-04
.219E-04
-062E-04
. 912E-04
.770E-04
, 635E-04
-507E-04
.385E-04
.268E-04
. 158E-04
. Q52E-04
. 952E-04
.857E-04
.766E-04
. 680E-04
.598E-04
. 520E-04
-446E-04
.376E-04
. 309E-04
-245E-04
.184E-04
. 126E-04
.071E-04
. 019E-04
.695E-05
.222E-05
.772E-05
.344E-05
-937E-05
.550E-05
-182E-Q5
. 332E-05
-499E-05
. 132E-05
-B80E-05
.593E-05
-321E-05
. 061E-05
-814E-05
.579E-05
-356E-05
. 144E-05
. 942E-05
. 749E-05
-567E-05
-393E-05
.227E-05
. 070E-05
. 920E-05
. 778E-05
-642E-05
-513E-05
.391E-05
D-37
-------
A Case Study
Table D-9. Northern Parcel Trichloroethene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
[Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
217B
2179
21SO
2181
21B2
2133
2184
21B5
2186
2187
2188
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.977E+05
1.977E+05
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E4-05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.243E-07
1.182E-Q7
1.124E-07
1.070E-07
1.017E-07
9.678E-08
9.206E-08
8.757E-08
8.330E-08
7.924E-03
7.537E-08
7.170E-08
6.820E-08
6.487E-08
6.171E-08
5.870E-08
5.534E-08
5.311E-08
5.052E-08
4.806E-08
4.572E-08
4.349E-08
4.137E-08
3. 935 E- 08
3.743E-08
3.560E-08
3.387E-08
3.222E-08
3.064E-08
2.915E-08
2.773E-08
2.638E-QS
2.509E-08
2.387E-08
2.270E-08
2.159E-08
2.054E-08
1.954E-08
1.859E-08
1.768E-08
1.632E-08
1.600E-08
1.522E-08
1.448E-08
1.377E-08
1.310E-08
1.246E-08
1.185E-08
1.127E-08
2.274E-05
2.163E-05
2.058E-05
1.957E-OS
1.8S2E-05
1.771E-05
1.685E-05
1.603E-05
1.524E-05
1.450E-05
1.379E-05
1.312E-05
1.248E-05
1.187E-05
1.129E-05
1.074E-OS
1.022E-05
9.720E-06
9.246E-06
8.795E-06
8.366E-06
7.958E-06
7.570E-06
7.201E-06
6.849E-06
6.515E-06
6.198E-06
5.895E-06
5.608E-06
5.334E-06
5.Q74E-06
4.627E-06
4.591E-06
4.367E-06
4.154E-06
3-952E-06
3.759E-06
3.576E-06
3.401E-06
3.235E-06
3.078E-06
2.928E-06
2.785E-06
2.649E-06
2.520E-06
2.397E-06
2.280E-06
2.169E-06
2.063E-06
D-38
-------
Rose Hill, Rl
Table D-10. Northern Parcel Vinyl Chloride Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177-1.000X030177-1.002\ROSEHI-1\NORTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** user Mode Selection *****
NMOG : 4500.00 ppmv ***** User Mode Selection *****
Methane : 56.0000 I volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : vinyl Chloride (HAP/TOO
Molecular Wt - 62.50 Concentration - 0.620000 ppmV
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year : 2003 Closure Year; 2004
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year : 13179.47 Mg/year
Model Results
Year
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1931
1982
1983
1984
1985
1986
1937
1988
1989
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
Refuse In Place {Mg)
1.318E+04
2.636E+04
3.954E+04
5.272E+04
6.590E+04
7.908E+04
9.226E+Q4
1.054E+05
1.186E+05
1.318E+05
1.450E+05
1.5B2E+05
1.713E+OS
1.845E+05
1. 977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-1-05
1.977E-t-05
1.977E+05
1.977E+05
Vinyl Chloride (HAP/VOC) Emission Rate
(Mg/yr) (Cubic m/yr)
3.224E-04
6.291E-04
9.208E-04
1.198E-03
1.462E-03
1.713E-03
1.952E-03
2.179E-03
2.396E-03
2.601E-03
2.797E-03
2.933E-03
3.160E-03
3.328E-03
3.488E-03
3.318E-03
3.156E-03
3.002E-03
2.856E-03
2.717E-03
2.584E-03
2.458E-03
2.338E-03
2.224E-03
2.116E-03
2.012E-03
1.914E-03
1.821E-03
1.732E-03
1.64BE-03
1.567E-03
1.491E-03
1.418E-03
1.349E-03
1.283E-03
1.221E-03
1.161E-03
1.104E-03
1.051E-03
9.994E-04
9.506E-04
9.043E-04
8.602E-04
8.182E-04
7.783E-04
1.240E-01
2.420E-01
3.542E-01
4.610E-01
5.625E-01
6.591E-01
7.510E-01
8.384E-01
9.215E-01
1,001E+00
1.076E+00
1.147E+00
1.215E+00
1.280E+00
1.342E+00
1.276E+00
1.214E+00
1.155E+00
1.099E-1-00
1.045E+00
9.940E-01
9.456E-01
8.995E-01
8.556E-01
8.139E-01
7.742E-01
7.364E-01
7.005E-01
6.663E-01
6.338E-01
6.029E-01
5.735E-01
5.455E-01
5.189E-01
4.936E-01
4.696E-01
4.467E-01
4.249E-01
4.042E-01
3.844E-01
3.657E-01
3.479E-01
3.309E-01
3.148E-01
2.994E-01
D-39
-------
A Case Study
Table D-10. Northern Parcel Vinyl Chloride Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2032
2083
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-KJ5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-I-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
7.4Q4E-04
7.042E-Q4
6.699E-04
6.372E-04
6.062E-04
5-766E-04
5.435E-04
5.217E-04
4.963E-04
4.721E-04
4.490E-04
4.271E-04
4.063E-04
3.865E-04
3.676E-04
3.497E-04
3.327E-04
3.1S4E-04
3.010E-04
2.863E-04
2.724E-04
2.591E-04
2.464E-04
2.344E-04
2.230E-04
2.121E-04
2.018E-04
1.919E-04
1.826E-04
1.737E-Q4
1.652E-04
1.571E-04
1.495E-04
1.422E-04
1.353E-04
1.287E-04
1.224E-04
1.164E-04
1.107E-04
1.053E-04
1.002E-04
9.531E-05
9.066E-05
8. 624 E- 05
8.203E-05
7.803E-05
7-423E-05
7.061E-05
6.716E-05
6.389E-05
6.077E-05
5.731E-05
5.499E-05
5.231E-05
4.976E-05
4.733E-05
4.502E-05
4.233E-05
4.074E-05
3.875E-05
3.696E-05
3.506E-05
3-335E-05
3.173E-05
3.018E-05
2.871E-05
2.731E-05
2.597E-05
2.471E-05
2.350E-05
2.236E-05
2.846E-01
2.709E-01
2.577E-01
2.451E-01
2.332E-01
2.218E-01
2.110E-01
2.007E-01
1.909E-01
1.316E-01
1.727E-01
1.643E-01
1.563E-01
1.487E-01
1.414E-01
1.345E-01
1.230E-01
1.217E-01
1.158E-01
1.101E-01
1.048E-01
9.966E-02
9.480E-02
9.Q18E-02
8.578E-02
8.160E-02
7.762E-02
7.383E-02
7.023E-02
6.631E-02
6.355E-02
6.045E-02
5.750E-02
5.470E-Q2
5.203E-02
4.949E-02
4.7Q8E-02
4.478E-02
4.260E-02
4.052E-02
3.854E-02
3.666E-02
3.488E-02
3.317E-02
3.156E-02
3.002E-02
2.855E-02
2.716E-02
2.584E-Q2
2.458E-02
2.338E-02
2.224E-02
2.115E-02
2.012E-02
1.914E-02
1.821E-02
1.732E-02
1.647E-02
1.567E-02
1.491E-02
1.418E-02
1.349E-02
1.283E-02
1.220E-02
1.161E-02
1.104E-02
1.050E-02
9.992E-03
9.505E-03
9.041E-03
8.600E-03
D-40
-------
Rose Hill, Rl
Table D-10. Northern Parcel Vinyl Chloride Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
20B4
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
2.
2.
1.
1,
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7 .
7 .
7 .
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3,
3.
3.
2,
2.
2,
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
9.
3,
8.
8.
7.
7 .
7.
127E-05
023E-OS
924 E- 05
830E-05
741E-05
656E-05
575E-05
499E-05
426E-Q5
356E-05
290E-05
227E-05
167E-05
110E-05
056E-05
005E-05
556E-06
090E-06
646E-06
225E-06
823E-Q6
442E-06
079E-06
734E-06
405E-06
093E-06
796E-OS
513E-06
244E-06
986E-06
745E-06
514E-06
294E-06
034E-06
835E-06
696E-06
515E-06
344E-06
181E-06
026E-Q6
878E-06
738E-06
604E-06
477E-06
356E-06
241E-06
132E-06
026E-06
929E-06
835E-06
746E-06
6S1E-06
5BOE-06
502E-06
429E-06
360E-Q6
293E-06
230E-06
170E-06
113E-06
059E-06
Q07E-06
5BOE-07
113E-07
669E-07
246E-07
844E-07
461E-07
097E-07
6.751E-07
6.
422E-07
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
.1B1E-03
.782E-Q3
. 402E-03
, 041E-03
.698E-03
-371E-03
. 060E-03
-765E-03
. 484E-03
.216E-03
. 962E-03
. 720E-03
.490E-03
-271E-03
. 062E-03
.864E-03
-676E-03
-497E-03
.326E-03
-164E-03
. Q10E-03
.363E-03
, 723E-03
-590E-03
.464E-03
.344E-03
.230E-03
. 121E-03
-017E-03
.919E-03
.825E-03
. 736E-03
. 652E-03
. 571E-03
-494E-03
. 422E-03
. 352E-03
-236E-03
.224E-03
. 164E-03
.107E-03
. 053E-03
.002E-03
.529E-04
.065E-04
. 622E-04
-202E-04
. 802E-04
-421E-Q4
. 060E-04
-715E-04
.338E-04
-076E-04
.7BOE-04
-498E-04
.230E-04
, 975E-04
.732E-04
-501E-04
.232E-04
.073E-04
. 874E-04
. 685E-04
-506E-04
.335E-04
. 172E-04
.017E-04
. B70E-04
-730E-04
-597E-04
. 470E-04
D-41
-------
A Case Study
Table D-10. Northern Parcel Vinyl Chloride Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-K05
1.977E+05
1.977E-<-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
6.109E-07
5.811E-07
5.527E-07
5.258E-07
5.001E-07
4-757E-07
4.525E-07
4.305E-07
4.095E-Q7
3.895E-07
3.705E-07
3.524E-07
3.353E-07
3.189E-07
3.033E-07
2.836E-07
2.745E-07
2.611E-07
2.484E-07
2.362E-07
2.247E-07
2.138E-07
2.033E-07
1.934E-07
1.840E-07
1.750E-07
1.665E-07
1.584E-07
1.506E-07
1.433E-07
1.363E-07
1.297E-07
1.233E-07
1.173E-07
1.116E-07
1.062E-07
1.010E-07
9.605E-OS
9.137E-08
S.691E-08
8.267E-08
7.864E-08
7.480E-08
7.116E-OS
6.769E-08
6.439E-08
6-125E-08
5.826E-OB
5.S42E-OB
2.350E-04
2.235E-04
2.126E-04
2.023E-04
1.924E-04
1.830E-04
1.741E-04
1.656E-04
1.575E-04
1.498E-04
1.425E-04
1.356E-04
1.290E-04
1.227E-04
1.167E-04
1.110E-04
1.056E-04
1.004E-04
9.554E-05
9.088E-05
S.645E-05
8.223E-05
7.822E-OS
7.441E-05
7.078E-05
6.733E-05
6.404E-05
6.092E-05
5.795E-05
5.512E-OS
5.243E-05
4.988E-05
4.744E-05
4.513E-05
4.293E-05
4.084E-05
3.884E-05
3.695E-05
3.515E-05
3.343E-05
3.180E-05
3.025E-05
2.878E-05
2.737E-05
2.604E-05
2.477E-05
2.356E-05
2.241E-05
2.132E-05
D-42
-------
Rose Hill, Rl
Table D-11. Northern Parcel m,p-Xylene Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\NORTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 1 volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : m,p-Xylene (HAP/VOC)
Molecular wt - 106.17 Concentration - 6.730000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Year
Refuse In Place {Mg)
m,p-Xylene (HAP/VQC) Emission Rate
(Mg/yr) (Cubic tti/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 31SE+04
. 636E+04
.954E+04
.272E+Q4
, 590E+04
. 908E+04
.226E+04
. 054E+05
. 186E+05
.318E+Q5
-450E+05
.5S2E+05
. 713E+05
.845E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
-977E+05
5.
1.
1,
2.
2,
3.
3.
4.
4.
4.
5.
5.
5.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
945E-03
160E-02
698E-02
210E-02
696E-02
159E-02
600E-02
019E-02
417E-02
796E-02
157E-02
500E-02
826E-02
137E-02
432E-02
118E-02
820E-02
536E-02
266E-02
009E-02
765E-02
532E-Q2
311E-02
101E-02
901E-02
711E-02
S30E-02
35GE-02
194E-02
038E-02
890E-02
749E-02
615E-02
437E-02
366E-02
251E-02
141E-02
037E-02
937E-02
843E-02
753E-02
667E-02
S86E-02
509E-02
435E-02
1
2
3
5
6
7
3
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
3
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
. 346E+00
. 627E+00
. 845E+00
. 004E+00
, 106E+00
.155E+00
. 152E+00
. 101E+00
. OOOE+01
.036E+01
. 168E+01
-246E+01
.319E+01
.390E+01
.457E+01
.335E+01
.318E+01
.254E+01
-193E+01
. 134E+01
-079E+01
. 026E+01
-763E+00
.287E+00
.834E+00
. 403E+00
. 994E+00
. 604E+00
-233E+00
. 880E+-00
, 545E+00
.225E+00
. 922E+00
. 633E+00
-358E+00
.097E+00
. 848E+00
. 612E+00
.387E+00
. 173E+00
. 970E+00
. 776E+00
-592E+00
, 417E+00
-250E+00
D-43
-------
A Case Study
Table D-11. Northern Parcel m,p-Xylene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.365E-02
1.299E-Q2
1.235E-02
1.175E-02
1.118E-02
1.063E-02
1.011E-02
9.620E-03
9.151E-03
8.705E-03
8.280E-03
7.876E-03
7.492E-03
"7.127E-03
6.779E-03
6.449E-Q3
6.134E-03
5.835E-03
5.550E-03
5.280E-03
5.Q22E-03
4.777E-03
4.544E-03
4.323E-03
4.112E-03
3.911E-03
3.721E-03
3.539E-03
3.366E-03
3.202E-03
3.046E-03
2.898E-03
2.756E-03
2.622E-03
2.494E-03
2.372E-03
2.257E-03
2.147E-03
2.042E-03
1.942E-03
1.848E-03
1.757E-03
1.672E-03
1.590E-03
1.513E-03
1.439E-03
1.369E-03
1.302E-03
1.238E-03
1.178E-03
1.121E-03
1.066E-03
1-014E-03
9.645E-04
9.175E-04
8.727E-04
8.302E-04
7.897E-04
7.512E-04
7.145E-04
6.797E-04
6.4S5E-04
6-150E-04
5.850E-04
5.565E-04
5.293E-04
5.035E-04
4.790E-04
4.556E-04
4.334E-04
4.122E-04
3.091E+00
2.941E+00
2.797E+00
2.661E+00
2.531E+00
2.408E+00
2.290E+00
2.179E+00
2.072E+00
1.971E-I-00
1.875E+00
1.784E+00
1.697E+00
1.614E+00
1.535E+00
1.460E+00
1.389E+00
1.321E+00
1.257E+00
1.196E+00
1.137E+00
1.082E+00
1.029E+00
9.789E-01
9.311E-01
8.857E-01
3.425E-01
8.014E-01
7.623E-01
7.252E-01
6.898E-01
6.562E-01
6.242E-01
5.937E-Q1
5.648E-01
5.372E-01
5.110E-01
4.861E-01
4.624E-01
4.396E-01
4.184E-01
3.980E-01
3.786E-01
3.601E-01
3.425E-01
3.258E-01
3.099E-01
2.946E-01
2.805E-01
2.S68E-01
2.538E-01
2.414E-01
2.296E-01
2.1B4E-01
2.Q78E-01
1.976E-01
1.880E-01
1.788E-01
1.701E-01
1.618E-01
1.539E-01
1.464E-01
1.393E-01
1.325E-01
1.260E-01
1.199E-01
1.140E-01
1.035E-01
1.032E-01
9.814E-02
9.335E-02
D-44
-------
Rose Hill, Rl
Table D-11. Northern Parcel m,p-Xylene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2034
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7.
7 .
7.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2,
2.
2.
2.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
921E-04
730E-Q4
548E-04
375E-04
211E-04
QS4E-04
905E-04
763E-04
629E-Q4
500E-04
378E-04
262E-04
152E-04
047E-04
947E-04
852E-04
762E-04
676E-04
594E-04
S17E-04
443E-04
372E-04
305E-04
242E-04
181E-04
123E-04
069E-04
017E-04
670E-05
198E-05
750E-05
323E-05
917E-05
531E-05
164E-05
814E-05
482E-05
166E-05
865E-05
579E-Q5
307E-05
048E-05
802E-05
568E-05
345E-05
133E-05
932E-05
740E-05
557E-05
334E-05
219E-05
062E-05
913E-05
771E-05
635 E- 05
5Q7E-05
385E-05
268E-05
158E-05
052E-05
952E-05
857E-Q5
767E-05
680E-05
598E-05
520E-05
446E-05
376E-05
309E-05
245E-05
184E-05
8
8
8
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
3
8
7
7
6
6
6
5
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
.830E-02
.447E-Q2
, 035E-02
, 643E-Q2
.270E-02
. 916E-02
.579E-02
-258E-02
. 953E-02
. 662E-02
-386E-02
-123E-02
.S74E-02
. 636E-02
.410E-02
.195E-02
-990E-02
-795E-02
. 610E-02
-434E-02
.267E-02
.107E-02
, 956E-02
-812E-02
. 675E-02
.544E-02
. 420E-02
.302E-02
. 190E-02
.083E-02
, 981E-02
. 885E-02
.793E-02
. 705E-Q2
. 622E-02
.543E-02
. 468E-02
-396E-02
.328E-02
.263E-02
.202E-02
. 143E-02
.087E-02
.034E-02
.839E-03
.360E-03
. 903E-03
. 469E-03
-056E-Q3
. 663E-03
-289E-03
. 934E-03
-596E-03
.274E-03
. 968E-03
.677E-03
-400E-03
.137E-03
-836E-03
. 648E-03
-421E-03
.206E-03
-OOOE-03
-805E-03
. 620E-03
. 443E-03
.275E-03
. 116E-03
. 964E-03
-819E-03
. 682E-03
D-45
-------
A Case Study
Table D-11. Northern Parcel m,p-Xylene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E-<-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.126E-05
1.071E-OS
1.019E-05
9.695E-06
9.222E-06
8-772E-06
8.345E-06
7.938E-06
7.551E-06
7.182E-06
6.832E-06
6.499E-06
6.182E-06
5.880E-06
5.594E-06
5.321E-06
5.061E-06
4.814E-06
4.580E-06
4.356E-06
4.144E-06
3.942E-06
3.749E-06
3.567E-06
3.393E-06
3.227E-06
3.070E-06
2.920E-06
2.778E-06
2.642E-06
2.513E-06
2.391E-06
2.274E-06
2.163E-06
2.058E-06
1.957E-06
1.862E-06
1.771E-06
1.685E-06
1.6Q3E-Q6
1.524E-06
1.450E-06
1.379E-06
1.312E-06
1.248E-06
1.187E-06
1-129E-06
1.074E-06
1.022E-06
2.551E-03
2.426E-03
2.308E-03
2.195E-03
2.088E-03
1.931E-Q3
1.390E-03
1.798E-03
1.710E-03
1.626E-03
1.547E-03
1.472E-03
1.400E-03
1.332E-03
1.267E-03
1.205E-03
1.146E-03
1.090E-03
1.037E-03
9.865E-04
9.334E-04
8.926E-04
8.491E-04
8.077E-04
7.633E-04
7.308E-04
6.952E-04
6.613E-04
6.290E-04
5.933E-04
5.692E-04
5.414E-04
5.150E-04
4.B99E-04
4.660E-04
4.433E-04
4.216E-04
4.011E-04
3.815E-04
3.629E-04
3.452E-04
3.284E-04
3.124E-04
2.971E-04
2.826E-04
2.S89E-04
2.557E-04
2.433E-04
2.314E-04
D-46
-------
Rose Hill, Rl
Table D-12. Northern Parcel o-Xylene Emisson Rate from Year 1968 to 2203.
Source: H:\3000V030177~1.000\030177~1.OD2\ROSEHI~1\NORTHERN.PRM
Model Parameters
Lo s 170.00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 4500.00 ppmv ***** user Mode Selection *****
Methane : 56.0000 $ volume
Carbon Dioxide : 44.0000 % volume
Air Pollutant : o-Xylene (HAP/VOC)
Molecular wt - 106.17 Concentration - 1.100000 ppmV
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2004
13179.47 Mg/year
Model Results
Year
Refuse In Place (Mg)
o-Xylene (HAP/VOC) Emission Rate
(Mg/yr) (Cubic m/yr)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1931
1982
1933
1984
19S5
1936
1987
1988
19B9
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1.318E+04
2.636E+Q4
3.954E+04
5.272E+04
6.590E+04
7.908E+04
9.226E+04
1.054E+05
1.186E+05
1.318E+05
1.450E+Q5
1.5B2E+05
1.713E+05
1.B45E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
9.717E-04
1.896E-03
2.775E-03
3.612E-03
4.407E-03
5.1S4E-03
5.884E-03
6.569E-03
7.220E-03
7.840E-03
8.429E-03
8.990E-03
9.523E-03
1.003E-02
1.051E-02
l.OOOE-02
9.512E-03
9.048E-03
8.607E-03
8.187E-03
7.788E-03
7.408E-03
7.047E-03
6.703E-03
6.376E-03
6.065E-03
5.770E-03
5.488E-03
5.220E-03
4.966E-03
4.724E-03
4.493E-03
4.274E-03
4.066E-03
3.867E-03
3.679E-03
3.499E-03
3.329E-03
3.166E-03
3.012E-03
2.865E-03
2.725E-03
2.592E-03
2.466E-03
2.346E-03
2.201E-01
4.294E-01
6.285E-01
8.179E-01
9.980E-01
1.169E+00
1.332E+00
1.4B7E+00
1.635E+00
1.775E+00
1.909E+00
2.036E+00
2.157E+00
2.271E+00
2.381E+00
2.265E+00
2.154E+00
2.049E+00
1.949E+00
1.854E+00
1.764E+00
1.678E+00
1.596E+00
1.518E+00
1.444E+00
1.374E+00
1.307E+00
1.243E+-00
1.182E+00
1.125E+00
1.070E+00
1.018E+00
9.679E-01
9.207E-01
8.758E-01
G.331E-01
7.925E-01
7.538E-01
7.170E-01
6.821E-01
6.488E-01
6.172E-01
5-871E-Q1
5.584E-01
5.312E-01
D-47
-------
A Case Study
Table D-12. Northern Parcel o-Xylene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
207S
2079
2030
2031
2082
2083
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+05
977E+OS
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+QS
977E-I-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
917E+05
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
B.
7.
7 .
7.
6.
6.
6.
5.
5.
5.
4.
4,
4.
4.
4,
3.
3.
3.
3.
3.
3.
2,
2.
2.
2.
2.
2,
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9,
9.
B.
8,
7 .
7.
7 .
6.
231E-03
122E-03
019E-03
921E-03
827E-03
738E-03
653E-03
572E-03
496E-03
423E-03
353E-03
287E-03
225E-03
165E-03
108E-03
054E-03
003E-03
537E-04
072E-04
629E-04
209E-04
808E-04
427E-04
065E-04
721E-04
393E-04
081E-04
784E-04
502E-04
234E-04
979E-04
736E-04
505E-04
2B5E-04
076E-04
877E-04
688E-04
508E-04
337E-04
175E-04
020E-04
872E-04
732E-04
599E-04
472E-04
352E-04
237E-04
128E-04
024E-04
925 E- 04
832E-04
742E-04
657E-04
576E-04
500E-04
426E-04
357E-04
291E-04
228E-04
168E-04
111E-04
057E-04
005E-04
562E-05
095E-05
652E-05
230E-05
B28E-05
447E-05
083E-05
738E-05
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
. 053E-01
.BQ6E-01
.572E-01
.349E-01
. 137E-01
. 935E-01
.743E-01
-561E-01
.387E-01
.222E-01
. 065E-01
. 915E-01
.773E-01
.638E-01
.509E-01
.387E-01
-270E-01
. 160E-01
.054E-01
. 954E-01
. 859E-01
. 768E-01
, 6S2E-01
. 600E-01
-522E-01
.448E-01
.377E-01
. 310E-01
-246E-01
.185E-01
.127E-01
-072E-01
. 020E-01
.704E-02
.231E-02
. 731E-02
-352E-02
. 945E-02
.558E-02
. 139E-02
-838E-02
. 505E-02
. 188E-02
.886E-02
.599E-02
.326E-02
.066E-02
. B19E-02
-584E-02
.360E-02
-148E-02
. 945E-02
-753E-02
.570E-02
.396E-02
.230E-02
.073E-02
. 923E-02
-780E-02
. 645E-02
-516E-02
. 393E-02
-276E-02
.165E-02
-060E-02
. 959E-02
-864E-02
. 773E-02
. 686E-02
. 604E-02
.526E-02
D-48
-------
Rose Hill, Rl
Table D-12. Northern Parcel o-Xylene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2084
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E-J-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
S.
6.
5.
5.
5.
4.
4.
4,
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
e.
7 ,
7.
7 .
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
409E-05
097E-OS
799E-05
517E-05
248E-05
992E-05
74GE-05
S17E-05
296E-Q5
037E-05
887E-05
698E-05
518E-05
346E-05
1B3E-05
028E-05
880E-05
739E-05
606E-05
479E-05
35SE-05
243E-05
134E-05
029E-05
930E-05
836E-05
747E-05
662E-05
581E-05
503E-05
430E-05
360E-05
294E-05
231E-05
171E-05
114E-05
059E-05
008E-05
586E-06
119E-Q6
674E-06
251E-06
849E-06
466E-06
102E-06
755E-06
426E-06
113E-06
814E-06
531E-06
261E-06
005E-06
760E-06
528E-06
307E-06
097E-Q6
898E-06
707E-06
S27E-06
355E-06
191E-06
035E-06
887E-06
747E-06
613E-06
485E-06
364E-06
249E-06
139E-06
035E-06
935 E- 06
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
5
4
4
4
.451E-02
.381E-Q2
.313E-02
.249E-02
.188E-02
. 130E-02
. 075E-02
. 023E-02
. 729E-03
.255E-03
. 803E-03
. 374E-03
.9S6E-03
-577E-03
.206E-03
.856E-03
-522E-03
-204E-03
. 901E-03
, 613E-03
. 340E-03
.079E-03
, 831E-03
-596E-03
.372E-03
.158E-03
. 956E-03
. 763E-03
-579E-03
.405E-03
.239E-03
. 081E-03
. 930E-03
. 787E-03
-652E-03
.522E-03
. 399E-03
-282E-03
.171E-03
. 065E-03
.964E-03
. 368E-03
.777E-03
.691E-03
.608E-03
.530E-03
-455E-03
.384E-03
-317E-Q3
.252E-03
-191E-03
. 133E-03
-078E-03
.025E-03
-754E-04
.279E-04
-826E-04
.396E-04
. 986E-04
.597E-04
-226E-04
. 374E-04
-539E-04
-220E-04
.916E-04
. 628E-04
.353E-04
. 092E-04
-844E-04
. 608E-04
. 383E-04
D-49
-------
A Case Study
Table D-12. Northern Parcel o-Xylene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
2202
2203
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E-<-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.841E-06
1.751E-06
1.666E-06
1.585E-06
1.507E-06
1.434E-06
1.364E-06
1.297E-06
1.234E-06
1.174E-06
1.117E-06
1.062E-06
1.010E-06
9.611E-07
9.143E-07
8.697E-07
8.272E-07
7.869E-07
7.485E-07
7.120E-07
6.773E-07
6.443E-07
6.128E-07
5.830E-07
5.545E-07
5.275E-07
5.01SE-07
4.773E-07
4.540E-07
4.319E-07
4.108E-07
3.908E-07
3.717E-07
3.536E-07
3.363E-07
3.199E-07
3.043E-07
2.895E-07
2.754E-07
2.619E-07
2.492E-07
2.370E-07
2.255E-07
2.145E-07
2.040E-07
1.940E-07
1-846E-07
1.756E-07
1.670E-07
4 . 169E-04
3.966E-04
3.772E-04
3.588E-04
3.413E-04
3.24'7E-04
3.039E-04
2.938E-04
2.795E-04
2.658E-04
2.529E-04
2.405E-04
2.238E-04
2.177E-04
2.070E-04
1.969E-04
1.873E-04
1.782E-04
1.S95E-04
1.612E-04
1.534E-04
1.459E-04
1.388E-04
1.320E-04
1.256E-04
1.194E-04
1.136E-04
1.081E-04
1.028E-04
9.780E-05
9.303E-05
8.849E-05
8.417E-05
B.Q07E-Q5
7.616E-05
7.245E-05
6.892E-05
6.556E-05
6.236E-05
5.932E-05
5.642E-05
5.367E-05
5.105E-05
4.856E-05
4.620E-05
4.394E-05
4.180E-05
3.976E-05
3.782E-05
D-50
-------
Rose Hill, Rl
Table D-13. Southern Parcel Methane Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000\030177~1.OD2\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo s 170.00 m"-3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 $ volume
Carbon Dioxide : 41.0000 % volume
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year : 2003 Closure Year: 2002
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year : 12238.07 Mg/year
Year
Model Results
Refuse In Place (Mg)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1981
1982
1983
1984
1935
1986
1987
1938
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
2013
2014
1.318E+04
2.636E+04
3.954E+04
5.272E+Q4
6.590E+04
7.9Q8E+04
9.226E+04
1.054E+05
1.136E+05
1.31BE+Q5
1.450E+05
1.5B2E+05
1.713E+05
1.845E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
Methane Emission Rate
[Mg/yr) [Cubic m/yr)
7.474E+01
1.458E+02
2.135E+02
2.77EE+02
3.390E+02
3.972E+02
4.525E+02
5.052E+02
5.553E+02
6.030E+02
6.483E+02
S.914E+02
7.324E+02
7.714E+02
8.086E+02
7.691Et02
7.316E+02
6.959E+02
6.620E+02
S.297E+02
5 . 990E+02
5 . 698E+02
5.420E+02
5.156E+02
4.904E+02
4.665Et02
4.437E+02
4.221E+02
4.015E+02
3.819E+02
3.633E+02
3.456E+02
3.287E+02
3.127E+02
2.975E+02
2.829E+02
2.691E+02
2.560E+02
2.435E+02
2.317E+02
2.204E+02
2.096E+02
1.994E+02
1.897E+02
1.804E+02
1.716E+02
1.632E+02
1
2
3
4
5
5
6
7
8
9
9
1
1
1
1
1
1
1
9
9
8
8
8
7
7
6
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
-120E+05
. 186E+05
.200E+05
.164E+05
-081E+05
.953E+05
. 733E+05
. 573E+05
.324E+05
. 036E+05
-717E+Q5
. 036E+06
.098E+06
-156E+06
-212E+06
. 153E+06
-Q97E+06
.043E+06
. 923E+05
.439E+05
-978E+05
.541E+05
-124E+05
.72GE+05
-351E+05
. 992E+05
. 651E+05
.327E+05
.018E+05
. 725E+-05
-446E+05
.180E+05
. 927E+05
, 687E+05
.459E+05
.241E+05
.034E+05
.83BE+05
. 650E+05
-472E+05
-303E+05
. 142E+05
-989E+05
. S43E+05
-704E+05
-572E+05
-447E+05
D-51
-------
A Case Study
Table D-13. Southern Parcel Methane Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2032
2083
2034
2085
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-KJ5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-HD5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.553E+02
1.477E+02
1.4Q5E+02
1.337E+02
1.271E+02
1-209E+02
1.150E+02
1.D94E+02
1.041E+02
9.901E+01
9.41BE+01
8.959E+01
8.522E+01
8.107E+01
7.711E+01
7.335E+01
6.977E+01
6.637E+01
6.313E+01
6.005E+01
5.713E+01
5.434E+01
5.169E+01
4-917E+01
4.677E+01
4.449E+01
4.232E+01
4.026E+01
3.829E+01
3.643E+01
3.465E+01
3.296E+01
3.135E+01
2.982E+01
2.837E+01
2.698E+01
2.567E+01
2.442E+01
2.323E+01
2.209E+01
2.102E+01
1.999E+01
1.902E+01
1.809E+01
1.721E+01
1.637E+01
1.557E+01
1.431E+01
1.409E+01
1.340E+01
1.275E+01
1.212E+01
1-153E+01
1.097E+01
1.044E+01
9.927EtOQ
9.443E+00
8.932E+00
8.544E+00
8.128E+00
7.731E+00
7.354E+00
6-995E+00
6.654E+00
6.330E+00
6.021E+00
5.727E+00
5.448E-I-00
5.182E+00
4.930E+00
4-689E+00
2.326E+05
2.214E+05
2.106E+05
2.003E+05
1.906E+05
1.813E+05
1.724E+05
1.640E+05
1.560E+05
1.484E+05
1.412E+05
1.343E+05
1.277E+05
1.215E+05
1.156E+05
1.099E+05
1.046E+05
9.948E+04
9.463E+04
9.002E+04
S.563E+04
8.145E+04
7.748E+04
7.370E+04
7.011E+04
6.669E+04
6.343E+04
6.034E+04
5.740E+04
5.460E+04
5.194E+04
4.940E+04
4.699E+04
4.470E+04
4.252E+04
4.045E+04
3.847E+04
3.660E+04
3.431E+04
3.312E+04
3.150E+04
2.996E+04
2.850E+04
2.711E+04
2.579E+04
2.453E+04
2.334E+04
2.220E+04
2.112E+04
2.009E+04
1.911E+04
1.817E+04
1.729E+04
1.644E+04
1.564E+04
1.488E+04
1.415E+04
1.346E+04
1.281E+04
1.218E+04
1.159E+04
1.102E+04
1.049E+04
9.974E+03
9.488E+03
9.025E+03
8.585E+03
8.166E+03
7.768E+03
7.389E+03
7.029E+03
D-52
-------
Rose Hill, Rl
Table D-13. Southern Parcel Methane Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
CMg/yr)
[Cubic m/yr)
2086
2087
20B8
2089
2090
2091
2092
2093
2094
2095
2096
2097
209S
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2113
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
2155
2156
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-1-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
4.
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
2.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
9.
9.
9.
8.
8.
7.
7 .
7.
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2,
2.
2.
1,
1.
1.
1.
1.
1.
1.
1.
460E+00
243E+00
036E+00
839E+00
652E+00
474E+00
304E+00
143E+00
990E+00
844E+00
705E+00
573E+00
448E+00
329E+00
215E-I-00
107E+00
004E+00
906E+00
813E+00
725E+00
641E+00
561E+00
465E+00
412E+00
343E+00
278E+00
216E+00
156E+OQ
100E+00
046E+00
953E-01
467E-01
006E-01
566E-01
149E-01
751E-01
373E-01
014E-01
671E-01
346E-01
037E-01
742E-01
462E-Q1
19SE-01
942E-01
701E-01
472E-01
254E-01
046E-01
849E-01
661E-01
493E-01
313E-01
151E-01
998E-01
851E-01
712E-01
530E-01
454E-01
335E-01
221E-01
112E-01
009E-Q1
911E-01
818E-01
730E-01
645E-01
565E-01
4S9E-01
416E-01
347E-01
6
. 636E+03
6.360E+03
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
3
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
. 050E+03
-755E+03
.474E+03
.207E+03
.953E+03
.711E+03
. 4S2E+03
-263E+03
-055E+03
. 857E+03
. 669E+03
.490E+03
.320E+03
.158E+03
-004E+03
.858E+03
. 718E+03
. 586E+03
. 460E+03
.340E+03
.226E+03
. 117E+03
-014E+03
. 916E+03
. 822E+03
. 733E+03
. 649E+03
.568E+03
-492E+03
-419E+03
.350E+03
.2B4E-1-03
-221E+03
.162E+03
-105E+03
-Q51E+03
.OOOE+03
.512E+02
-048E+02
. 607E+02
. 187E+02
. 788E+02
, 408E+02
.047E+02
.703E+02
.376E+02
-065E+02
. 770E+02
-488E+02
.220E+02
-966E+02
.724E1-02
, 493E+02
.274E+02
.066E+02
.867E+02
-679E+02
. 499E+02
-329E+02
. 166E+02
-012E+02
.865E+02
. 725E+02
.592E+02
. 466E+02
.346E+02
-231E+02
. 122E+02
.019E+02
D-53
-------
A Case Study
Table D-13. Southern Parcel Methane Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
[Cubic m/yr)
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2131
2192
2183
2184
2185
2186
2187
2188
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1,
1.
1,
1.
1.
1.
1.
1.
1.
1,
1,
1.
1.
1.
1.
1.
1.
1,
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1,
1.
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-S-05
977E+05
977E+05
977E+05
977E+05
977E+05
917E+05
977E+05
977E+05
1.
1.
1.
1.
1.
9.
9.
9.
8.
8.
7,
7.
7.
6.
5.
&.
5.
5.
5.
4,
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
I.
1.
1,
1.
1,
1.
1.
281E-01
219E-01
159E-01
103E-01
049E-01
97SE-02
492E-02
029E-02
589E-02
170E-02
771E-02
392E-02
032E-02
689E-02
363E-02
052E-02
757E-02
476E-02
209E-02
955E-02
713E-02
484E-02
265E-02
057E-02
859E-02
671E-02
492E-02
322E-02
160E-02
005E-02
859E-02
719E-02
587E-02
461E-02
341E-02
226E-02
118E-02
Q15E-02
916E-02
823E-02
734E-02
649E-02
569E-02
492E-02
420E-02
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
. 921E+02
.627E+02
. 738E+02
, 653E+02
. 572E+02
. 496E+02
.423E+02
-353E-I-02
.287E+02
-225E+02
.165E+02
-108E+02
. 054E+Q2
.003E-J-02
.537E-I-01
.Q72E4-01
. 629B+01
.209E+01
. 908E+01
.427E+01
. 065E-<-01
. 721E-1-01
-393E+01
-081E+01
.784E+01
.502E+01
.234E-)-01
.979E+01
-736E+01
.505E+01
-285E+01
.076E+01
. 877E+01
. 638E+01
. 508E+01
.337E+01
-175E+01
-020E+01
-872E+01
. 732E+01
.599E+01
.472E+01
-352E+01
.237E+01
. 128E+01
D-54
-------
Rose Hill, Rl
Table D-14. Southern Parcel NMOC Emisson Rate from Year 1968 to 2203.
Source: H:\3000V030177~1.000\030177~1.OD2\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo s 170.00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 $ volume
Carbon Dioxide : 41.0000 % volume
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year : 2003 Closure Year: 2002
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year : 12238.07 Mg/year
Year
Model Results
Refuse In Place (Mg)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1981
1982
1983
1984
1935
1986
1987
1938
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
2013
2014
1.318E+04
2.636E+04
3.954E+04
5.272E+04
6.590E+04
7.9Q8E+04
9.226E+04
1.054E+05
1.136E+05
1.31BE+Q5
1.450E+05
1.5B2E+05
1.713E+05
1.845E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
NMOC Emission Rate
[Mg/yr) [Cubic m/yr)
1.736E+00
3.386E+00
4 . 957E+00
6.451E+00
7.871E+00
9.223E+00
1.051E+01
1.173E+01
1.290E+01
1.400E+01
1.505E+01
1.606E+01
1.7Q1E+01
1.791E+01
1.878E+01
1.796Et01
1.699E+01
1.616E+01
1.537E+01
1.4€2E+01
1.391E+01
1.323E+01
1.259E+01
1.197E+01
1.139E+01
1.083Et01
1.030E+01
9.802E+00
9.324E+00
0.869E+00
8.437E+00
8.025E+00
7 . 634E+00
7.261E+00
6.907E+00
6.570E+00
6.250E+00
5.945E+00
5.655E+00
5.379E+00
5.117E+00
4.868E+00
4 . 630E+00
4.404E+00
4.190E+00
3.985E+00
3.791E+00
4
9
1
1
2
2
2
3
3
3
4
4
4
4
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
-842E+02
. 447E+02
.333E+03
.800E+03
.196E+03
.573E+03
. 932E+03
-273E+03
.598E+03
. 906E+03
-200E+Q3
. 479E+03
.745E+03
-998E+03
-238E+03
. 933E+03
-740E+03
.509E+03
-289E+03
.079E+03
. 881E+03
. 691E+03
-511E+03
.340E+03
-177E+03
. 022E+03
-875E+03
.735E+03
. 601E+03
. 474E+-03
-354E+03
.239E+03
-130E+03
.026E+03
.927E+03
. 333E+03
.744E+03
.659E+03
.578E+03
-501E+03
. 428E+03
. 358E+03
-292E+03
.229E+03
-169E+03
-112E+03
-058E+03
D-55
-------
A Case Study
Table D-14. Southern Parcel NMOC Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2032
2083
2034
2085
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-J-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
3.606E+00
3.430E+00
3.263E4-00
3.104E+00
2.952E+00
2-808E+00
2.671E-I-00
2.541E+00
2.417E+00
2.299E-I-00
2.137E+00
2.030E+OQ
1.979E+00
1.832E+00
1.791E+00
1.703E+00
1.620E+00
1.541E+00
1.466E+00
1.395E+00
1.327E+00
1.262E+00
1.200E+00
1-142E+00
1.036E+00
1.033E+00
9.827E-01
9.348E-01
8.892E-01
8.458E-01
8.046E-01
7.654E-01
7.230E-01
6.925E-01
6.587E-01
6.266E-01
5.961E-01
5.670E-01
5.393E-01
5.130E-01
4.880E-01
4.642E-01
4.416E-01
4.200E-01
3.995E-01
3.801E-01
3.615E-01
3.439E-01
3.271E-01
3.112E-Q1
2.960E-01
2.816E-01
2-678E-01
2.54SE-01
2.423E-01
2.305E-01
2.193E-01
2.036E-01
1.981E-01
1.837E-01
1.795E-01
1.708E-01
1-624E-01
1.545E-01
1.470E-01
1.398E-01
1.330E-01
1.265E-01
1.203E-01
1.145E-01
1.089E-01
1.006E+03
9.569E+02
9.103E+02
8.S59E+02
8.236E+02
7.835E+02
7.453E+02
7.089E+02
6.743E+02
S.414E+02
6.102E+02
5-S04E+02
5.521E+02
5.252E+02
4. 996E+02
4.752E+02
4.520E+02
4.300E+02
4.090E+02
3.891E+02
3.701E+02
3.520E+02
3.349E+02
3.185E+02
3.030E+02
2.882E+02
2.742E+02
2.608E+02
2.481E+02
2.360E+02
2.245E+02
2.135E+02
2.031E+02
1.932E+02
1.838E+02
1.748E+02
1.663E+02
1.582E+02
1.505E+02
1.431E+02
1.361E+02
1.295E+02
1.232E+02
1.172E+02
1,115E+02
1.060E+02
1.009E+02
9.594E+01
9.126E+01
8.681E+01
8.258E+01
7.855E+01
7.472E+01
7.107E+01
6.761E+01
6.431E+01
6.117E+01
5.319E+01
5.535E+01
5.265E+01
5.009E+01
4.764E+01
4.532E+01
4.311E+01
4.101E+01
3.901E+01
3.710E+01
3.529E+01
3.357E+01
3.194E+01
3.038E+01
D-56
-------
Rose Hill, Rl
Table D-14. Southern Parcel NMOC Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2086
20B7
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
2155
2156
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+Q5
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
1.
9.
9.
8,
B.
8.
7.
7,
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
4,
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
9.
9.
8.
8.
8.
7.
7 .
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
036E-01
853E-02
372E-02
915E-02
490E-02
067E-02
673E-02
299E-02
943E-Q2
605E-02
282E-02
976E-02
6S5E-02
407E-02
144E-02
893E-Q2
65 4 E- 02
427E-02
211E-02
006E-Q2
810E-02
625 E- 02
448E-02
280E-02
120E-02
968E-02
823E-02
685E-02
554E-02
430E-02
311E-02
198E-02
091E-02
989E-02
892E-02
800E-02
712E-02
629E-02
549E-02
474E-02
402E-02
333E-02
268E-02
207E-02
148E-02
092E-02
038E-02
878E-03
396E-03
938E-03
502E-03
088E-03
693E-03
318E-03
961E-03
622E-03
299E-03
991E-03
699E-03
421E-03
157E-03
905E-03
666E-03
439E-03
222E-03
016E-03
820E-03
634E-03
457E-03
288E-03
128E-03
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
.890E+01
.749E+01
. 615E+01
, 487E+01
.366E+01
-250E+01
. 141E+01
-036E+01
. 937E+01
.843E+01
. 753E+01
. 667E+01
.586E+01
. 509E+01
.435E+01
.365E+01
-298E+01
-23SE+01
. 175E+01
-118E+01
. 063E+01
.011E+01
, 619E+00
. 150E+00
.704E+00
.279E+00
. 375E+00
. 491E+00
. 126E+00
.778E+00
.448E+00
. 133E+00
. 834E+00
. 550E+00
-279E+00
. 021E+00
. 777E+00
-544E+00
.322E+00
. 111E+00
. 911E+00
. 720E+00
.539E+00
.366E+00
.202E+00
.046E+00
-897E+00
. 756E+00
. 621E+00
. 494E+00
-372E+00
.256E+00
. 146E+00
.042E+00
. 942E+00
.847E+00
-757E+00
. 672E+00
-590E+00
.512E+00
-439E+00
. 369E+00
-302E+00
-238E+00
.178E+00
. 120E+00
. 066E+00
. 014E+00
-644E-01
-173E-01
.726E-01
D-57
-------
A Case Study
Table D-14. Southern Parcel NMOC Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
2188
2189
2190
2191
2192
2193
2194
2195
219S
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+OS
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E-J-05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+05
977E+05
977E+05
2.
2.
2.
2.
2.
2-
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
9.
9.
8.
8.
B.
7.
7,
6.
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
975E-03
830E-03
692E-03
561E-03
436E-03
317E-03
204E-03
097E-03
994E-Q3
897E-03
805E-03
717E-03
633E-03
553E-03
477E-03
405E-03
337E-03
272E-03
210E-03
151E-03
095E-03
041E-03
904 E- 04
421E-04
961E-04
524E-04
109E-04
713E-04
337E-04
979E-Q4
639E-04
315E-04
007E-04
714E-04
435E-04
170E-04
918E-04
678E-04
450E-04
233E-04
027E-04
830E-04
643E-04
466E-04
297E-04
3
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
.300E-01
.S96E-01
.511E-01
. 144E-01
.796E-01
. 464E-01
. 149E-Q1
-849E-01
.564E-Q1
.293E-01
. 034E-01
. 789E-01
.555E-01
-333E-01
.122E-01
.921E-01
-730E-01
-548E-01
.375E-01
-210E-01
. 054E-01
. 905E-01
, 763E-01
. 628E-01
.500E-01
.378E-01
.262E-01
. 152E-01
-047E-01
.947E-01
.852E-01
. 762E-01
. 676E-01
. 594E-01
-516E-01
. 442E-01
. 372E-01
.305E-01
.241E-01
. 181E-01
.123E-01
. 069E-01
.016E-01
. 669E-02
.197E-02
D-58
-------
Rose Hill, Rl
Table D-15. Southern Parcel Benzene Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 1 volume
Carbon Dioxide : 41.0000 % volume
Air Pollutant : Benzene (HAP/VOC)
Molecular wt - 76.12 Concentration - 0-240000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2002
1223S.07 Mg/year
Model Results
Year
Refuse In Place {Mg)
Benzene {HAP/VOC) Emission Rate
(Mg/yr) (Cubic m/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 31SE+04
. 636E+04
.954E+04
.272E+Q4
, 590E+04
. 908E+04
.226E+04
. Q54E+05
. 186E+05
.318E+05
.450E+05
.5S2E+05
. 713E+05
.845E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
-977E+05
1.
2.
4.
5.
6,
7.
S.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
S.
7.
7.
7 .
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
481E-04
839E-04
229E-04
503E-04
716E-04
869E-04
966E-04
OQ1E-03
100E-03
195E-03
284E-03
370E-03
451E-03
528E-03
602E-03
524E-03
449E-03
379E-03
312E-03
248E-03
187E-03
129E-03
074E-03
021E-03
716E-04
242E-04
791E-04
363E-04
955E-04
567E-04
198E-04
847E-04
513E-04
195E-04
893E-04
606E-04
332E-04
072E-04
825E-04
5B9E-04
366E-04
153E-04
950E-04
758E-04
574E-04
4
8
1
1
2
2
2
3
3
3
3
4
4
4
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
.557E-02
. 392E-02
-302E-01
. 694E-01
, 067E-01
.422E-01
. 759E-01
. 080E-01
.386E-01
. 676E-01
. 953E-01
-216E-01
.466E-01
. 704E-01
.930E-01
. S90E-01
.461E-01
.243E-01
-036E-01
. 340E-01
. 652E-01
. 474E-01
-305E-01
. 144E-01
. 990E-01
. 344E-01
-706E-01
. 574E-01
-448E-01
.329E-01
.215E-01
.107E-01
. 004E-01
. 907E-01
. 814E-01
.725E-01
. 641E-01
.561E-01
.485E-01
. 412E-01
.344E-01
.278E-01
-216E-01
, 156E-01
-100E-01
D-59
-------
A Case Study
Table D-15. Southern Parcel Benzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
3.400E-04
3.234E-Q4
3.076E-04
2.926E-04
2.734E-04
2-648E-04
2.519E-04
2.396E-04
2.279E-04
2.1S8E-04
2.062E-04
1.962E-04
1.866E-04
1.775E-04
1.638E-04
1.606E-04
1.528E-04
1.453E-04
1.332E-04
1.315E-04
1.251E-04
1.190E-04
1.132E-04
1.077E-04
1.024E-04
9.741E-05
9.266E-05
8.814E-05
8.384E-05
7.975E-05
7.536E-05
7.216E-05
6.864E-05
6.530E-05
6.211E-05
5.908E-05
5.620E-05
5.346E-05
5.085E-05
4.837E-05
4.601E-05
4.377E-05
4.163E-05
3.960E-05
3.767E-05
3.584E-05
3-409E-05
3.243E-05
3.084E-05
2.934E-05
2.791E-05
2.655E-05
2-525E-05
2.402E-05
2.285E-05
2.174E-05
2.068E-05
1.967E-05
1.871E-05
1.780E-05
1.693E-05
1.610E-05
1-532E-05
1.457E-05
1.386E-05
1.318E-05
1.254E-05
1.193E-05
1.135E-05
1.079E-05
1-027E-05
1.046E-01
9.954E-02
9.468E-02
9.006E-02
8.567E-02
8.149E-02
7.752E-02
7.374E-02
7.014E-02
6.672E-02
6.347E-02
6-037E-02
5.743E-02
5.463E-02
5 . 196E-02
4.943E-02
4.702E-02
4.472E-02
4.254E-02
4.047E-02
3.S49E-02
3.662E-02
3.483E-02
3.313E-02
3.152E-02
2.998E-02
2.852E-02
2.713E-02
2.580E-02
2.455E-02
2.335E-02
2.221E-02
2.113E-02
2.010E-02
1.912E-02
1.818E-02
1.730E-02
1.645E-02
1.565E-02
1.439E-02
1.416E-02
1.347E-02
1.281E-02
1.219E-02
1,159E-02
1.103E-02
1.049E-02
9.979E-03
9.493E-03
9.030E-03
8.589E-03
8.170E-03
7.772E-03
7.393E-03
7.032E-03
6.689E-03
6.363E-03
6.053E-03
5.758E-03
5.477E-03
5.210E-03
4.956E-Q3
4.714E-03
4.484E-03
4.265E-03
4.057E-03
3.859E-03
3.671E-03
3.492E-03
3.322E-03
3.160E-03
D-60
-------
Rose Hill, Rl
Table D-15. Southern Parcel Benzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2034
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
9.
9.
8.
8,
7.
7.
7.
6,
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
9.
9.
8.
8.
8.
7 .
7.
6.
6.
e.
5.
5.
5.
5.
4,
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
766E-06
290E-Q6
837E-06
406E-06
996E-06
606E-06
235E-06
882E-06
547E-Q6
227E-06
924 E- 06
635 E- 06
3SOE-06
098E-06
350E-06
613E-06
388E-06
174E-06
971E-06
777E-06
593E-Q6
418E-06
251E-06
092E-06
942E-06
798E-06
662E-OS
532E-06
408E-06
291E-06
179E-06
073E-06
972E-06
876E-06
784E-Q6
697E-06
614E-06
536E-06
461E-06
3B9E-Q6
322E-06
257E-06
196E-06
138E-06
082E-06
029E-06
792E-07
314E-07
860E-07
428E-07
017E-07
626E-07
254E-07
900E-07
563E-07
243E-07
939E-07
649E-07
374E-07
112E-07
862E-07
625E-07
40DE-07
185E-07
981E-07
787E-07
602E-07
426E-07
259E-07
100E-07
949E-07
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
.006E-03
.859E-Q3
. 720E-03
.587E-03
.461E-03
-341E-03
.227E-03
-118E-03
. 015E-03
. 917E-03
. 823E-03
. 734E-03
.650E-03
-569E-03
.493E-03
.420E-03
-351E-03
-235E-03
.222E-03
-162E-03
. 106E-03
.052E-03
, 001E-03
-517E-04
.053E-04
. 612E-04
. 192E-04
. 792E-04
-412E-04
.051E-04
.707E-04
. 380E-04
. 068E-04
. 772E-04
-491E-04
.223E-04
. 968E-04
-726E-04
.496E-04
.276E-04
.068E-04
. 369E-04
.681E-04
.501E-04
.330E-04
.168E-04
. 014E-04
. B67E-04
-727E-Q4
.594E-04
-467E-04
.347E-04
-232E-04
.124E-04
-020E-04
. 921E-04
-828E-04
.739E-04
. 654E-04
.573E-04
-496E-04
. 423E-04
-354E-04
-288E-04
.225E-04
. 165E-04
.109E-04
. 055E-04
-003E-04
-542E-05
.076E-05
D-61
-------
A Case Study
Table D-15. Southern Parcel Benzene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-J-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+05
977E+05
977E+05
977E+05
977E+05
2.
2.
2.
2.
2.
2-
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1,
1.
1.
1.
9.
9.
8.
8.
8.
7 .
7.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2-
8Q5E-07
669E-07
538E-07
415E-07
297E-07
185E-07
07BE-07
977E-07
8BOE-Q7
789E-07
702E-07
619E-07
540E-07
465E-07
393E-07
325E-07
261E-07
199E-07
141E-07
085E-07
032E-07
817E-08
338E-08
883E-08
449E-03
037E-08
645E-08
273E-08
918E-08
580E-08
260E-08
95 4 E- 08
664E-08
338E-03
125E-08
875E-08
637E-08
411E-OS
196E-08
991E-08
797E-08
611E-08
435E-08
268E-08
108E-08
95 7 E- 08
813E-QB
8
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
. 634E-05
.213E-Q5
. 812E-05
. 431E-05
.069E-05
-724E-05
.396E-Q5
-084E-05
. 7B7E-Q5
.505E-05
-237E-05
. 981E-05
.738E-05
-507E-05
.2B7E-05
.078E-05
-879E-05
-690E-OS
.510E-05
-339E-05
. 176E-05
. 021E-05
, 874E-OS
-734E-05
. 600E-05
.474E-05
.353E-05
.238E-05
-129E-05
.025E-OS
, 926E-05
. 833E-05
.743E-05
. 658E-Q5
.577E-05
.500E-05
. 427E-05
.358E-05
.291E-05
.226E-05
.168E-05
. 111E-05
.057E-05
. 006E-05
.567E-06
.100E-06
. 656E-06
D-62
-------
Rose Hill, Rl
Table D-16. Southern Parcel Chlorobenzene Emisson Rate from Year 1968 to 2203.
Source: H:\3000V030177~1.000\030177~1.002\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo s 170.00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 $ volume
Carbon Dioxide : 41.0000 % volume
Air Pollutant : Chlorobenzens (HAP/VOC)
Molecular wt - 112.56 Concentration - 0.720000 ppmV
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2002
12238.07 Mg/year
Model Results
Year
Refuse In Place (Mg)
Chlorobenzene (HAP/VOC) Emission Rate
(Mg/yr) [Cubic m/yr)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1931
1982
1933
1984
19S5
1936
1987
1988
19B9
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
I
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 318E+04
. 636E+Q4
. 954E+04
.272E+04
.590E+04
. 908E+04
.226E+04
. 054E+05
. 186E+05
. 318E+05
.450E+05
.5B2E+05
. 713E+05
.B45E+05
. 977E+Q5
. 977E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
, 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
-977E+05
-977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
6.
1.
1.
2.
2.
3.
3.
4.
4.
5.
5,
5.
6.
6.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4,
3.
3.
3.
3.
3.
3.
2.
2,
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
400E-04
249E-03
828 E- 03
379E-03
903E-03
401E-03
875E-03
326E-03
755E-03
1S4E-03
552E-03
921E-03
272E-03
606E-03
924E-03
537E-03
265E-03
960E-G3
669E-03
393E-03
130E-03
879E-03
641E-03
415E-03
200E-03
995E-03
800E-03
615E-03
438E-03
271E-03
111E-03
960E-03
815E-03
678E-03
S47E-03
423E-03
305E-03
192E-03
086E-03
934E-03
887E-03
795E-03
708E-03
624 E- 03
545E-03
1
2
3
5
6
7
8
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
8
7
7
6
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
.367E-01
.668E-01
. 905E-01
.031E-01
-200E-01
-265E-01
.278E-01
.241E-01
-016E+QO
. 103E+00
.186E+00
-265E+00
. 340E+00
. 411E+00
. 479E+00
.407E+00
-338E+00
.273E+00
-211E+00
. 152E+00
-096E+00
.042E+00
. 914E-01
. 431E-01
. 971E-01
.533E-01
.117E-01
. 721E-01
-345E-01
.936E-01
-646E-01
.322E-01
.013E-01
. 720E-01
.441E-01
.176E-Q1
. 923E-01
-633E-01
-455E-01
.237E-01
-031E-01
. 834E-01
-647E-Q1
-469E-01
-300E-01
D-63
-------
A Case Study
Table D-16. Southern Parcel Chlorobenzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2032
2083
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.470E-03
1.398E-03
1.330E-03
1.265E-03
1.203E-03
1-145E-Q3
1.033E-03
1.036E-03
9.851E-04
9.371E-04
8.914E-04
8.479E-04
8.066E-04
"7.672E-04
7.296E-04
6.942E-04
6.604E-04
6.232E-04
5.975E-04
5.6S4E-04
5.407E-04
5.143E-04
4.892E-04
4.653E-04
4.427E-04
4.211E-04
4.005E-04
3.810E-04
3.624E-04
3.447E-04
3.279E-04
3.119E-04
2.967E-04
2.822E-04
2.635E-04
2.554E-04
2.429E-04
2.311E-04
2.198E-04
2.091E-04
1.9S9E-04
1.892E-04
1.800E-04
1.712E-04
1.628E-04
1.549E-04
1-473E-04
1.402E-04
1.333E-04
1.268E-04
1.206E-04
1.148E-04
1-092E-04
1.038E-04
9.877E-05
9.395E-05
8.93TE-05
8.501E-05
8.037E-05
7.692E-05
7.317E-05
6.960E-05
6 - 621 E- 05
6.298E-05
5.991E-05
5.698E-05
5.421E-05
5.156E-05
4.905E-05
4.666E-05
4.438E-05
3.139E-01
2.986E-Q1
2.B40E-01
2.702E-01
2.570E-01
2.445E-01
2.326E-Q1
2.212E-01
2.104E-01
2.002E-01
1.904E-01
1.811E-01
1.723E-01
1.639E-01
1.559E-01
1.433E-01
1.411E-01
1.342E-01
1.276E-01
1.214E-01
1.155E-01
1.099E-01
1.045E-01
9.940E-02
9.455E-02
8.994E-02
3.555E-02
8.138E-02
7.741E-02
7.364E-02
7.004E-02
6.663E-02
6.338E-02
S.029E-02
5.735E-02
5.455E-02
5.189E-02
4.936E-02
4.695E-02
4.466E-02
4.248E-02
4.041E-02
3.644E-02
3.657E-02
3.478E-02
3.309E-02
3.147E-02
2.994E-02
2.848E-02
2.709E-02
2.577E-02
2.451E-02
2.332E-02
2.218E-02
2.110E-02
2.007E-02
1.909E-02
1.316E-02
1.727E-02
1.643E-02
1.563E-02
1.437E-Q2
1.414E-02
1.345E-02
1.280E-02
1.217E-02
1.158E-02
1.101E-02
1.048E-02
9.966E-03
9.479E-03
D-64
-------
Rose Hill, Rl
Table D-16. Southern Parcel Chlorobenzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2034
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
4.
4.
3.
3,
3.
3.
3.
2.
2.
2.
2.
Z.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
G.
7.
7 .
6.
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2,
2.
2.
2.
2,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
222E-05
016E-OS
820E-05
634E-05
456E-05
288E-05
127E-05
975E-05
83GE-Q5
692E-05
560E-05
436E-05
317E-05
204E-05
096E-05
994E-05
897E-05
804E-05
716E-05
633E-05
553E-05
477E-05
4 05 E- 05
337E-05
272E-05
209E-05
151E-05
094E-05
041E-05
903E-06
420E-06
960E-06
523E-06
107E-06
712E-Q6
336E-06
978E-06
638 E- 06
314E-06
006E-Q6
713E-06
435E-06
170E-06
917E-06
678E-06
449E-06
232E-06
026E-06
830E-06
643E-06
465E-06
296E-06
135E-06
933E-06
837E-06
699E-Q6
567E-06
442E-06
323E-06
210E-06
102E-06
999E-06
902E-06
809E-06
721E-06
S37E-06
557E-06
431E-06
409E-06
340E-06
275E-06
9
8
8
1
1
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
9
3
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
.017E-03
.577E-Q3
. 159E-03
, 761E-03
.333E-03
-023E-03
. 630E-03
-354E-03
. 044E-03
.750E-03
. 469E-03
-202E-03
.949E-03
-707E-03
.47SE-03
.259E-03
-052E-03
-854E-03
. 666E-03
-487E-03
. 317E-03
.155E-03
, 002E-03
-85SE-03
.716E-03
.5S3E-03
. 457E-03
. 338E-03
-224E-03
.115E-03
.012E-03
. 914E-03
. 321E-03
. 732E-03
-647E-03
.567E-03
. 491E-03
-418E-03
.349E-03
.233E-03
.220E-03
. 161E-03
.104E-03
.050E-03
, 991E-04
.504E-04
. 041E-04
. SOOE-04
-180E-Q4
. 731E-04
-402E-04
. 041E-04
. 697E-04
.371E-04
-060E-04
.764E-04
-483E-04
.216E-04
. 962E-04
. 720E-04
-489E-04
.270E-04
-062E-04
-864E-04
. 676E-04
. 496E-04
.326E-04
. 164E-04
-009E-04
-863E-04
.723E-04
D-65
-------
A Case Study
Table D-16. Southern Parcel Chlorobenzene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-J-05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+05
977E+05
977E+05
977E+05
977E+05
1.
1.
1.
1.
9.
9.
B.
8.
8.
1 .
7.
6.
6.
6.
6.
5.
5.
5,
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
213E-06
153E-06
097E-06
044E-06
928 E- 07
444E-07
933E-07
545E-07
128E-Q7
732E-07
355E-07
996E-07
655E-07
330E-07
022E-07
728E-07
449E-07
183E-07
930E-07
690E-07
461E-07
243E-07
036E-07
840E-07
652E-07
474E-07
305E-07
144E-07
990E-07
644E-07
706E-07
574E-07
446E-07
329E-07
215E-07
1Q7E-07
004E-07
907E-07
814E-07
7 25 E- 07
641E-07
561E-07
485E-07
413E-07
344E-07
278E-07
216E-07
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
.590E-04
.464E-Q4
.344E-04
.229E-04
.121E-04
. 017E-04
. 919E-04
-825E-04
. 736E-04
. 652E-04
-571E-04
. 494E-04
.422E-04
-352E-04
.2B6E-04
.223E-04
-164E-04
-107E-04
. 053E-04
-002E-04
.529E-05
.064E-05
, 622E-OS
-2Q1E-05
.801E-05
.421E-05
. 059E-05
. 715E-05
-387E-05
.076E-OS
.779E-05
. 498E-05
.229E-05
. 974E-05
-732E-05
.501E-05
-281E-05
.073E-05
.874E-05
. 635E-05
.505E-05
. 334E-05
.172E-05
. 017E-05
.870E-05
.730E-05
-597E-OS
D-66
-------
Rose Hill, Rl
Table D-17. Southern Parcel Chloroethane Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 1 volume
Carbon Dioxide : 41.0000 % volume
Air Pollutant : Chloroethane (HAP/VOC)
Molecular wt - 64.52 Concentration - 0-320000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2002
1223S.07 Mg/year
Model Results
Year
Refuse In Place {Mg)
Chloroethane (HAP/VOC) Emission Rate
(Mg/yr) (Cubic tti/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 31SE+04
. 636E+04
.954E+04
.272E+Q4
, 59QE+04
. 908E+04
.226E+04
. Q54E+05
. 186E+05
.318E+Q5
.450E+05
.582E+05
. 713E+05
.845E+05
.977E+Q5
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
-977E+05
1.
3.
4.
6.
7 .
8.
9.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8,
8.
7 .
7 .
7.
6.
6.
e.
5.
5.
5.
5.
4.
4.
4.
4.
3.
631E-04
132E-04
657E-04
060E-04
395E-04
665 E- 04
873E-04
102E-03
212E-03
315E-03
414E-03
508E-03
598E-03
633E-03
764E-03
678E-03
596E-03
518E-03
444E-03
374E-03
307E-03
243E-03
182E-03
125E-03
070E-03
018E-03
681E-04
209E-04
760E-04
333E-04
926E-04
540E-04
172E-04
822E-04
4B9E-04
173E-04
872E-04
586E-04
313E-04
054E-04
807E-04
573E-04
350E-04
138E-04
936E-04
6
1
1
2
2
3
3
4
4
4
5
5
5
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
. 076E-02
. 1SSE-01
. 735E-01
.258E-01
-756E-01
.229E-01
. 679E-01
. 107E-01
-51SE-01
. 902E-01
-270E-01
. 621E-01
.954E-01
.272E-01
.573E-01
.253E-01
. 948E-01
. 658E-01
-382E-01
. 119E-01
-870E-01
. 632E-01
-406E-01
. 191E-01
. 987E-01
. 793E-01
-608E-01
. 432E-01
-264E-01
. 105E-01
. 954E-01
.810E-01
. 673E-01
.542E-01
. 418E-01
.300E-01
. 188E-01
. 081E-01
.980E-01
. 333E-01
. 791E-01
. 704E-01
-621E-01
, 542E-01
. 467E-01
D-67
-------
A Case Study
Table D-17. Southern Parcel Chloroethane Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
3.744E-04
3.561E-04
3.388E-04
3.223E-04
3.065E-04
2-916E-04
2.774E-04
2.638E-04
2.510E-04
2.387E-04
2.271E-04
2.160E-04
2.055E-04
1.955E-04
1.859E-04
1.7S9E-04
1.682E-04
1.600E-04
1.522E-04
1.448E-04
1.377E-04
1.310E-04
1.245E-04
1.186E-04
1.128E-04
1.Q73E-04
1.020E-04
9.706E-05
9.233E-05
8.782E-05
8.354E-05
•7.947E-05
7.559E-05
7.191E-05
6.840E-05
6.506E-05
6.189E-05
5.887E-05
5.600E-05
5.327E-05
5.067E-05
4.820E-05
4.585E-05
4.361E-05
4.149E-05
3.946E-05
3-754E-05
3.571E-05
3.397E-05
3.231E-05
3.073E-05
2.923E-05
2-7B1E-05
2.645E-05
2.516E-05
2.394E-05
2.27TE-05
2.166E-05
2.060E-05
1.960E-05
1.864E-05
1.773E-05
1.687E-05
1.604E-05
1.526E-05
1.452E-05
1.381E-05
1.314E-05
1.250E-05
1.189E-05
1-131E-05
1.395E-01
1.327E-01
1.262E-01
1.201E-01
1.142E-01
1.087E-01
1.034E-01
9.832E-02
9.352E-02
8.396E-02
8.462E-02
8-050E-02
7.657E-02
7.284E-02
6. 926E-02
6.590E-02
6.269E-02
5.963E-02
5.672E-02
5.396E-02
5.133E-02
4.882E-02
4.644E-02
4.418E-02
4.202E-02
3.997E-02
3.902E-02
3.617E-02
3.440E-02
3.273E-02
3.113E-02
2.961E-02
2.817E-02
2. 679E-Q2
2.549E-02
2.424E-02
2.306E-02
2.194E-02
2.087E-02
1.935E-02
1.888E-02
1.796E-02
1.708E-02
1.625E-02
1.546E-02
1.471E-02
1.399E-02
1.331E-02
1.266E-02
1.204E-02
1.145E-02
1.089E-02
1.036E-02
9.857E-03
9.376E-03
8.919E-03
8.484E-03
8.070E-03
7.677E-03
7.302E-03
6.946E-03
6.607E-Q3
6.285E-03
5.979E-03
5.687E-03
5.410E-03
5.146E-03
4.395E-03
4.656E-03
4.429E-03
4.213E-03
D-68
-------
Rose Hill, Rl
Table D-17. Southern Parcel Chloroethane Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2034
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
1.
1.
9.
9.
8.
8.
7.
7,
7.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4,
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7.
7 .
7.
6.
6,
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
075E-05
023E-05
731E-06
257E-06
805E-06
376E-06
967E-06
S79E-06
209E-Q6
858E-06
523E-06
205E-06
902E-06
614E-06
341E-06
030E-Q6
832E-06
597E-06
373E-06
159E-06
956E-Q6
763E-06
S80E-06
4QSE-06
239E-06
081E-06
931E-OS
738E-06
652E-06
523E-06
400E-06
233E-06
171E-06
Q65E-06
965E-06
869E-06
778E-06
691E-06
609E-06
530E-06
455E-06
335E-06
317E-06
253E-06
192E-06
134E-06
078E-06
026E-06
756E-07
231E-07
828E-07
397E-07
988E-07
59BE-07
228E-07
875E-07
S40E-07
221E-07
918E-07
629E-07
354E-07
093E-07
845E-07
609E-07
334E-07
170E-07
967E-07
773E-07
589E-07
414E-07
248E-07
4
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
8
7
7
6
6
6
5
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
.OOBE-03
.812E-Q3
. 626E-03
, 449E-03
.281E-03
. 121E-03
. 969E-03
-824E-03
. 636E-03
.555E-03
. 431E-03
. 312E-03
.199E-03
-092E-03
. 990E-03
.893E-03
-801E-03
-713E-03
. 629E-03
-550E-03
. 474E-03
.402E-03
-334E-03
-269E-03
.207E-03
.148E-03
. 092E-03
. Q39E-03
-883E-04
.401E-04
, 942E-04
. 506E-04
. 091E-04
. 697E-04
-321E-04
. 964E-04
. 625E-04
-301E-04
.994E-04
. 702E-04
.424E-04
. 159E-04
. 908E-04
.668E-04
.441E-04
.224E-04
. 018E-04
. 822E-04
-636E-Q4
. 458E-04
-290E-04
. 129E-04
. 977E-04
.S31E-04
.693E-04
.562E-04
-437E-04
.318E-04
-205E-04
. 098E-04
. 995E-04
. B96E-04
-805E-04
-717E-04
. 634E-04
. 554E-04
.478E-04
. 406E-04
-337E-04
-272E-04
.210E-04
D-69
-------
A Case Study
Table D-17. Southern Parcel Chloroethane Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
[Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2161
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
21B2
2183
2184
2185
2186
2187
2138
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1,
1.
1,
1.
1.
1.
1.
1.
1.
1,
1,
1.
1.
1.
1.
1.
1.
1,
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1,
1.
1.
1.
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+OS
977E+05
977E+Q5
977E+05
977E+05
977E+D5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
3.
2.
2.
2.
2.
2.
2,
2,
2.
1,
1.
I.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
9,
9.
8.
8.
8.
7,
7.
6,
6.
6.
5.
5,
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
089E-07
939E-07
795E-07
659E-07
529E-07
406E-07
2S9E-07
177E-07
071E-07
970E-07
874E-07
782E-07
695E-07
613E-07
534E-07
459E-07
388E-07
320E-07
256E-07
19SE-07
136E-07
081E-07
028E-07
782E-08
305E-08
asiE-oa
419E-08
009E-03
618E-08
246E-08
893E-08
557E-03
237E-08
933E-03
644E-08
368E-OS
107E-08
857E-08
621E-08
395E-03
181E-08
977E-03
783E-08
598E-03
423E-08
256E-03
097E-08
1
1
1
9
9
8
3
8
7
7
6
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
. 151E-04
.Q95E-04
.042E-04
-908E-05
. 425E-05
. 965E-05
.528E-05
-112E-05
. 717E-05
-340E-05
. 982E-05
. 642E-05
. 318E-05
-010E-05
.717E-05
.438E-05
-173E-05
-920E-05
. 680E-05
.452E-05
.235E-05
. 028E-05
-832E-05
-645E-05
.467E-05
.298E-05
.137E-05
.934E-05
-839E-05
.700E-05
-569E-05
.443E-05
.324E-05
.211E-05
-103E-05
. OOOE-05
. 903E-05
-810E-05
-722E-05
. 638E-05
.558E-05
.432E-05
-410E-05
.341E-05
-276E-05
.213E-05
.154E-05
D-70
-------
Rose Hill, Rl
Table D-18. Southern Parcel Dichlorobenzene Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000\030177~1.002\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo : 170.00 tv^3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 St volume
Carbon Dioxide : 41.0000 % volume
Air Pollutant : Dichlorobenzene (VOC/HAP for 1,4 isomer)
Molecular wt - 147.00 Concentration - 0.190000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year : 2003 Closure Year: 2002
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year : 12238.07 Mg/year
Model Results
Year
Refuse In Place
Dichlorobenzene (VOC/HAP for 1,4 isomer) Emission Ra
(Mg) (Mg/yr) (Cubic m/yr)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1983
1984
1985
1986
1937
1988
1989
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
200S
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
I
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
.313E+04
. 636E+Q4
. 9S4E+04
.272E+04
. 590E+04
. 908E+Q4
. 226E+04
. 054E+05
. 186E+OS
. 318E+05
. 4SOE+05
.S82E+Q5
.713E+05
. 845E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+Q5
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+OS
. 977E+05
. 977E+05
. 977E+05
. 977E+OS
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
2.
4.
6.
8.
1,
1.
1.
1.
1,
1.
1.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1-
1.
1.
1.
9.
9.
8.
G.
7.
7.
7,
6.
6.
6.
5.
5,
5.
206E-04
304E-04
300E-04
198E-04
OOOE-03
172E-03
336E-03
491E-03
639E-03
780E-03
913E-03
041E-03
162E-03
277E-03
386E-03
270E-03
159E-03
054E-03
954E-03
858E-03
768E-03
682E-Q3
600E-03
522E-03
447E-03
377E-03
310E-03
246E-03
185E-03
127E-Q3
072E-03
020E-03
702E-04
229E-04
779E-04
351E-G4
943E-04
556E-04
187E-04
837E-04
SQ3E-04
1S6E-04
885E-04
598E-04
325E-04
3
7
1
1
1
1
2
2
2
2
3
3
3
3
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
, 608E-02
. 039E-02
. 030E-01
.341E-01
, 636E-01
. 917E-01
. 184E-01
. 439E-01
. S80E-01
. 911E-01
. 129E-01
. 337E-01
.535E-01
. 724E-01
. 903E-01
. 713E-01
. 532E-01
.359E-01
. 195E-01
. 040E-01
. 891E-01
. 750E-01
. 616E-01
. 489E-01
. 367E-01
.252E-01
. 142E-01
. 038E-01
, 938E-01
. 844E-01
. 754E-01
. 668E-01
-587E-01
. 509E-01
.436E-01
.366E-01
.299E-01
.236E-01
. 176E-01
. 118E-01
-064E-01
. 012E-01
. 625E-02
. 155E-02
. 709E-02
D-71
-------
A Case Study
Table D-18. Southern Parcel Dichlorobenzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
5.065E-04
4.818E-Q4
4.583E-04
4.359E-04
4.147E-04
3-945E-04
3.752E-04
3.569E-04
3.395E-04
3.230E-04
3.072E-04
2.922E-04
2.790E-04
2.644E-04
2.515E-04
2.392E-04
2.276E-04
2.1S5E-04
2.059E-04
1.959E-04
1.863E-04
1.772E-04
1.686E-04
1.604E-04
1.526E-04
1.451E-04
1.380E-04
1.313E-04
1.249E-04
1.188E-04
1.130E-04
1.075E-04
1.023E-04
9.727E-05
9.253E-05
8.801E-05
8.372E-05
7.964E-05
7.576E-05
7.206E-05
6.855E-05
6.520E-05
6.202E-05
5.900E-05
5.612E-05
5.338E-05
S-078E-05
4.830E-05
4.595E-05
4.371E-05
4.158E-05
3.955E-05
3-762E-05
3.578E-05
3.404E-05
3.238E-05
3.080E-05
2.930E-05
2.787E-05
2. 65 IE- 05
2-522E-05
2.399E-05
2-282E-05
2.170E-05
2.065E-05
1.964E-05
1.868E-05
1.777E-05
1.690E-05
1.608E-05
1.529E-05
8.234E-02
7.880E-02
7.496E-02
7.130E-02
6.782E-02
6.452E-02
6.137E-02
5.838E-02
5.553E-02
5.282E-02
5.024E-02
4-779E-02
4.546E-02
4.325E-02
4.114E-02
3.913E-02
3.722E-02
3.541E-02
3.36SE-02
3.204E-02
3.047E-02
2.899E-02
2.757E-02
2.623E-02
2.495E-02
2.373E-02
2.258E-02
2.148E-02
2.043E-02
1.943E-02
1.848E-02
1.758E-02
1.672E-02
1.591E-Q2
1.513E-02
1.440E-02
1.369E-02
1.303E-02
1.239E-02
1.179E-02
1.121E-02
1.066E-02
1.014E-02
9.649E-03
9.179E-03
8.731E-03
8.305E-03
7.900E-03
7.515E-03
7.148E-03
6.800E-03
6.468E-03
6.153E-03
5.S53E-03
5.567E-03
5.296E-03
5.037E-03
4.792E-03
4.558E-03
4.336E-03
4.124E-03
3.923E-Q3
3.732E-03
3.550E-03
3.377E-03
3.212E-03
3.055E-03
2.906E-03
2.765E-03
2.630E-03
2.502E-03
D-72
-------
Rose Hill, Rl
Table D-18. Southern Parcel Dichlorobenzene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2034
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
1.
1.
1.
1.
1.
1.
1.
1,
9.
9.
8.
8.
7 .
7.
7 .
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
8.
7 .
7,
6.
6.
6,
5.
5.
5.
5.
4.
4.
4.
455E-05
384E-OS
316E-05
252E-05
191E-05
133E-05
07BE-05
025E-05
752E-Q6
277E-06
824E-06
394E-06
985E-06
595E-06
225E-06
872E-Q6
537E-06
218E-06
915E-06
627 E- 06
352E-Q6
091E-06
843E-06
6Q7E-06
332E-06
168E-06
9S5E-OS
772E-06
S88E-06
413E-06
246E-06
038E-06
937E-06
794E-06
658E-06
528E-06
405E-06
238E-06
176E-06
070E-06
969E-06
873E-06
782E-06
695E-06
612E-06
533E-06
459E-06
336E-06
320E-06
255E-06
194E-06
136E-06
D81E-06
028E-06
778E-07
3Q1E-07
847E-07
416E-07
005E-07
615E-07
243E-07
890E-07
554E-07
234E-07
930 E- 07
S41E-07
366E-07
104E-07
855E-07
619E-07
393E-07
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
3
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
.330E-03
.263E-Q3
. 153E-03
, 048E-03
.948E-03
.853E-03
. 763E-03
-677E-03
.595E-03
.517E-03
. 443E-03
. 373E-03
.306E-03
-242E-03
.1B2E-03
.124E-03
-Q69E-03
-017E-03
. 674E-04
-203E-04
. 754E-04
.327E-04
, 921E-04
-534E-04
.167E-04
.817E-04
. 485E-04
. 169E-04
-868E-04
.582E-04
.309E-04
. 051E-04
. 804E-Q4
. 570E-04
-347E-04
. 135E-04
. 933E-04
-742E-04
.559E-04
.335E-04
.220E-04
. 063E-04
. 914E-04
.772E-04
.637E-04
.508E-04
-386E-04
.269E-04
-159E-Q4
. 053E-04
-953E-04
. 858E-04
-767E-04
.631E-04
-599E-04
.521E-04
-447E-04
.376E-04
-309E-04
.245E-04
-185E-04
. 127E-04
-Q72E-04
-020E-04
. 699E-05
.226E-05
.776E-05
.348E-05
. 941E-05
-554E-05
.186E-05
D-73
-------
A Case Study
Table D-18. Southern Parcel Dichlorobenzene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
21S1
2182
2183
21B4
2185
2186
2187
2188
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1,
977E+Q5
977E+OS
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+Q5
977E+Q5
977E+05
977E+05
977E+QS
977E+05
977E+QS
977E+05
977E+05
977E+OS
977E+05
977E+05
9T7E+Q5
977E+05
977E+05
977E+05
9T7E+05
977E+05
917E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-I-05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
4.
3.
3.
3.
3.
3.
3.
2,
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
G.
7.
7 .
6.
6.
6.
5.
5.
5.
5.
4,
4.
4.
4.
179E-07
975E-07
781E-07
597E-07
422E-07
255E-07
096E-07
945E-07
801E-07
6S5E-07
535E-07
411E-07
294E-07
162E-07
075E-07
974E-07
878E-07
786E-07
699E-07
616E-07
537E-07
462E-07
391E-07
323E-07
259E-07
197E-Q7
139E-07
083E-07
031E-07
803E-03
325E-08
870E-08
437E-08
026E-08
634E-08
2S2E-08
908E-08
571E-08
251E-08
946E-03
656E-08
380E-08
118E-08
S68E-03
631E-08
405E-08
190E-08
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
3
e
7
7
7
6
. 835E-05
.5Q2E-05
.185E-05
. S83E-05
.596E-05
-323E-05
. 064E-05
-817E-05
.582E-05
-358E-05
. 146E-05
. 944E-05
. 751E-05
.568E-05
. 394E-05
.229E-05
-Q71E-05
. 921E-05
. 779E-05
. 643E-05
.514E-05
. 392E-05
-275E-05
.164E-05
.059E-05
. 958E-05
. 863E-05
. 772E-05
. 686E-05
. 603E-05
.525E-05
-451E-05
, 380E-05
. 313E-05
.249E-05
. 188E-05
-130E-05
.075E-05
.022E-05
, 725E-06
-250E-06
. 799E-06
-370E-06
. 962E-06
.574E-06
.204E-06
.853E-06
D-74
-------
Rose Hill, Rl
Table D-19. Southern Parcel Toluene Emisson Rate from Year 1968 to 2203.
Source: H:\3000V030177~1.000\030177~1.OD2\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo s 170.00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 $ volume
Carbon Dioxide : 41.0000 % volume
Air Pollutant : Toluene (HAP/VOC)
Molecular wt - 92.14 Concentration - 2.550000 ppmV
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2002
12238.07 Mg/year
Model Results
Year
Refuse In Place (Mg)
Toluene (HAP/VOC) Emission Rate
(Mg/yr) (Cubic m/yr)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1931
1982
1933
1984
19S5
1936
1987
1988
19B9
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
I
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 318E+04
. 636E+Q4
. 954E+04
.272E+04
.590E+04
. 9Q8E+04
.226E+04
. 054E+05
. 186E+05
. 318E+05
.450E+05
.5B2E+05
. 713E+05
.B45E+05
. 977E+Q5
. 977E+Q5
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
, 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
-977E+05
-977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
1.
3.
5.
6.
8.
9.
1.
1.
1.
1.
1.
1.
1.
1.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
9.
8.
8,
7 .
7.
7.
6.
6.
6.
5.
5,
5.
4.
4.
4.
856E-03
621E-03
3 00 E- 03
897E-03
416E-03
861E-03
124E-02
254E-02
379E-02
4 97 E- 02
610E-02
717E-02
818E-02
915 E- 02
007E-02
910E-02
816E-02
728E-02
644E-02
5S3E-02
487E-02
415E-02
346E-02
2BOE-02
218E-02
158E-02
102E-02
04BE-02
969E-03
433E-03
020E-03
580E-03
162E-03
7S4E-03
385E-03
025E-03
682E-03
356E-03
046E-03
751E-03
471E-03
204E-03
950E-03
709E-03
479E-03
4
9
1
1
2
2
2
3
3
3
4
4
4
4
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
. 842E-01
.447E-01
.383E+00
.800E+00
. 196E+00
. 573E+00
. 932E+00
.273E+00
-598E+00
. 906E+00
.200E+00
-479E+00
. 745E+00
. 998E+00
-23SE+00
. 9B3E+00
. 740E+00
.509E+00
-289E+00
. 079E+00
. 881E+00
. 691E+00
-511E+00
. 340E+00
-177E+00
. 022E+00
.875E+00
. 735E+-00
-601E+00
.474E+00
-354E+00
.239E+QO
. 130E+QO
. 026E+00
. 927E+00
.833E+00
.744E+00
-659E+00
-578E+00
.501E+00
-428E+00
. 358E+00
-292E+QO
-229E+00
-169E+00
D-75
-------
A Case Study
Table D-19. Southern Parcel Toluene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
4.261E-03
4.053E-03
3.855E-03
3.667E-03
3.438E-03
3-318E-Q3
3.156E-03
3.003E-03
2.856E-03
2.717E-03
2.584E-03
2.458E-03
2.33SE-03
2.224E-03
2.116E-03
2.013E-03
1.914E-03
1.821E-03
1.732E-03
1.648E-03
1.567E-03
1.491E-03
1.418E-03
1.349E-03
1.233E-03
1.221E-03
1.1S1E-03
1.105E-03
1.051E-03
9.995E-04
9.507E-04
9.043E-04
S.602E-04
8.133E-04
•7.784E-04
7.404E-04
7.043E-04
6.700E-04
6.373E-04
6.062E-04
5.766E-04
5.4B5E-04
5.218E-04
4.963E-04
4.721E-04
4.491E-04
4-272E-04
4.0S3E-04
3.865E-04
3.677E-04
3.497E-04
3.327E-04
3-165 E-04
3.010E-04
2.863E-04
2.724E-04
2.591E-04
2.465E-04
2.344E-04
2.230E-04
2.121E-04
2.018E-04
1.919E-04
1.826E-04
1.737E-04
1.652E-04
1.572E-04
1.495E-04
1.422E-04
1.353E-04
1.287E-04
1.112E+00
1.058E+00
1.006E+00
9.569E-01
9.103E-01
8.659E-01
S.236E-01
7.835E-01
7.453E-01
7.089E-01
6.743E-01
6-414E-01
6.102E-01
5.804E-01
5.521E-01
5.252E-01
4.996E-01
4.752E-01
4.520E-01
4.300E-01
4.090E-01
3.891E-01
3.701E-01
3.520E-01
3.349E-01
3.185E-01
3.030E-01
2.832E-01
2.742E-01
2.6Q8E-01
2.481E-01
2.360E-01
2.245E-01
2.135E-Q1
2.031E-01
1.932E-01
1.838E-01
1.748E-01
1.663E-01
1.532E-01
1.505E-01
1.431E-01
1.361E-01
1.295E-01
1.232E-01
1.172E-01
1.115E-01
1.060E-01
1.009E-01
9.594E-02
9.126E-02
8.631E-02
8.258E-02
7.855E-02
7.472E-02
7.107E-02
6.761E-02
6.431E-02
6-117E-02
5.819E-02
5.535E-02
5.265E-02
5.009E-02
4.764E-02
4.532E-02
4.311E-02
4.101E-02
3.901E-02
3.710E-02
3.529E-02
3.357E-02
D-76
-------
Rose Hill, Rl
Table D-19. Southern Parcel Toluene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2034
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
1.
1.
1.
1,
1.
9.
5.
8.
e.
7.
7 .
7.
6.
6.
e.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7.
7 .
7 .
6.
6.
6.
5.
5.
5,
4.
4.
4.
4.
4.
3.
3.
224E-04
164E-Q4
1Q7E-04
053E-04
002E-04
532E-05
067E-05
625 E» 05
204E-Q5
804E-05
423E-05
061E-05
717E-05
389E-05
078E-05
731E-05
493E-05
231E-05
976E-05
733E-05
502E-05
233E-05
074E-05
875E-05
636E-05
507E-05
336E-05
173E-05
018E-05
871E-05
731E-05
598E-05
471E-05
35GE-05
236E-05
127E-05
023E-05
924 E- 05
831E-05
741E-05
656E-05
576E-05
499E-05
426E-05
356E-05
290E-05
227E-05
167E-05
110E-05
056E-05
005E-05
556E-06
D90E-06
647E-06
225E-06
824E-Q6
443E-06
030E-06
734E-06
406E-06
093E-06
796E-06
514E-06
245E-06
989E-06
746E-06
514E-06
294E-06
085E-06
885E-06
696E-06
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
3
8
7
7
7
.194E-02
.038E-Q2
. 390E-02
, 749E-Q2
.615E-02
-487E-02
.366E-02
-250E-02
. 141E-02
.036E-02
. 937E-02
. S43E-02
.753E-02
. 667E-02
.536E-02
.509E-02
-435E-02
-365E-02
.298E-02
-235E-02
. 175E-02
.118E-02
, 063E-02
-011E-02
. 619E-03
.150E-03
. 704E-03
.279E-03
-875E-03
.491E-03
.126E-03
6.778E-03
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
. 448E-03
. 133E-03
-834E-03
.550E-03
-279E-03
-021E-03
.777E-03
. 544E-03
.322E-03
. 111E-03
. 911E-03
.720E-03
.539E-03
.366E-03
-202E-03
. 046E-03
-897E-Q3
. 756E-03
. 621E-03
. 494E-03
-372E-03
.256E-03
-146E-03
.042E-03
, 942E-03
.347E-03
-757E-03
. 672E-03
-590E-03
.512E-03
-439E-03
-369E-03
.3Q2E-03
.238E-03
.178E-03
. 120E-03
-066E-03
-014E-03
. 644E-04
D-77
-------
A Case Study
Table D-19. Southern Parcel Toluene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E-J-05
977E+Q5
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+05
977E+05
977E+05
977E+05
977E+05
3.
3.
3.
3.
2.
2-
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7.
7.
7.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3-
516E-06
344E-06
181E-06
026E-06
87SE-06
738E-06
604E-06
477E-06
357E-Q6
242E-06
132E-06
028E-06
929E-06
835E-06
746E-06
661E-06
580E-06
503E-06
429E-06
360E-06
293E-06
230E-06
170E-06
113E-06
059E-06
007E-06
581E-07
114E-07
669E-07
247E-07
844E-07
462E-07
098E-07
752E-07
422E-07
1Q9E-07
811E-07
528E-07
258E-07
OQ2E-Q7
758E-07
526E-07
305E-07
095E-07
895E-07
705E-07
525E-07
9
8
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
.173E-04
.726E-Q4
.300E-04
. 896E-04
.511E-04
. 144E-04
. 796E-04
-464E-04
. 149E-04
.849E-04
-564E-04
.293E-Q4
.034E-04
-789E-04
.555E-04
.333E-04
-122E-04
. 921E-04
. 730E-04
-548E-04
. 375E-04
.210E-04
, Q54E-04
-905E-04
.763E-04
. 628E-04
.500E-04
. 378E-04
-262E-04
.152E-04
.047E-04
. 947E-04
. 852E-04
. 762E-Q4
.676E-04
.594E-04
. 516E-04
.442E-04
.372E-04
.305E-04
.241E-04
. 1B1E-04
.123E-04
. 069E-04
.016E-04
.S69E-05
-197E-OS
D-78
-------
Rose Hill, Rl
Table D-20. Southern Parcel Trichloroethene Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 1 volume
Carbon Dioxide : 41.0000 % volume
Air Pollutant : Trichloroethene (HAP/VOC)
Molecular wt - 131.36 Concentration - 0.030000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2002
1223S.07 Mg/year
Model Results
Year
Refuse In Place {Mg)
Triohloroethene (HAP/VOC) Emission Rate
(Mg/yr) (Cubic m/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 31SE+04
. 636E+04
.954E+04
.272E+Q4
, 59QE+04
. 908E+04
.226E+04
. 054E+05
. 186E+05
.318E+05
.450E+05
.582E+05
. 713E+05
.845E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
.977E+05
3.
6.
8,
1.
1.
1.
1.
2.
2.
2.
2.
2.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2,
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7 .
7.
113E-05
074E-05
890E-05
157E-04
412E-04
654E-04
885E-04
104E-04
313E-04
511E-04
700E-04
880E-04
050E-04
213E-04
368E-04
203E-04
047E-04
898E-04
757E-04
623E-04
495E-04
373E-Q4
257E-04
147E-04
042E-04
943E-04
848E-04
75GE-04
672E-04
591E-04
S13E-04
439E-04
369E-04
302E-04
239E-04
178E-04
121E-04
066E-04
014E-04
64SE-05
178E-Q5
730E-05
304E-05
899E-05
514E-05
5
1
1
2
2
3
3
3
4
4
4
5
5
5
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
. 696E-03
. 111E-02
. 627E-02
. 117E-02
-584E-02
.027E-02
. 449E-02
. S51E-02
-232E-02
.596E-02
. 941E-02
.270E-02
.582E-02
. 380E-02
.163E-02
. 862E-02
.576E-02
.304E-02
-045E-02
. 799E-02
-565E-02
.343E-02
-131E-02
. 929E-02
.738E-02
. 555E-02
-382E-02
.217E-02
-060E-02
. 911E-02
, 769E-02
. 634E-02
.506E-02
.383E-02
-267E-02
.157E-02
. 051E-02
. 951E-02
.856E-02
. 766E-02
.679E-02
.59BE-02
-520E-02
, 446E-02
-375E-02
D-79
-------
A Case Study
Table D-20. Southern Parcel Trichloroethene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
7.147E-05
6.799E-OS
6.467E-05
6.152E-05
5.852E-05
5-S66E-Q5
5.295E-05
5.037E-05
4.791E-05
4.557E-05
4.335E-05
4.124E-05
3.923E-05
3.731E-05
3.549E-05
3.376E-05
3.212E-05
3.055E-OS
2.906E-05
2.764E-05
2.629E-05
2.501E-05
2.379E-05
2.263E-05
2.153E-05
2.048E-05
1.948E-05
1.853E-05
1.763E-05
1.677E-05
1.595E-05
1.517E-05
1.443E-05
1.373E-05
1.306E-05
1.242E-05
1.181E-05
1.124E-05
1.069E-05
1.017E-05
9.673E-06
9.201E-06
8.753E-06
8.326E-06
7.920E-06
7.533E-06
7-166E-06
6.816E-06
6.484E-06
6.168E-06
5.867E-06
5.531E-06
5-309E-06
5.050E-06
4.803E-06
4.5S9E-Q6
4.346E-06
4.134E-06
3.933E-06
3.741E-06
3-559E-06
3.335E-06
3-220E-06
3.063E-06
2.913E-06
2.771E-06
2.636E-06
2.50SE-06
2.385E-Q6
2.269E-06
2.158E-06
1.306E-02
1.244E-02
1.1B4E-02
1.126E-02
1.071E-02
1.019E-02
9.690E-03
9.217E-03
8.768E-03
8.340E-03
7.933E-03
7.546E-03
7.178E-03
6.828E-03
6.495E-03
6.179E-03
5.877E-03
5.591E-03
5.318E-03
5.059E-03
4.312E-03
4.577E-03
4.354E-03
4.142E-03
3.940E-03
3.747E-03
3.565E-03
3.391E-03
3.225E-03
3.068E-03
2.919E-03
2.776E-03
2.641E-03
2.512E-03
2.389E-03
2.273E-03
2.162E-03
2.057E-03
1.956E-03
1.361E-03
1.770E-03
1.6B4E-03
1.602E-03
1.524E-03
1.449E-03
1.379E-03
1.311E-03
1.247E-03
1.187E-03
1.129E-03
1.074E-03
1.021E-03
9.715E-04
9.241E-04
8.790E-04
8 . 362E-04
7.954E-04
7.566E-04
7.197E-04
6.346E-04
6.512E-04
6.194E-04
5.892E-04
5.605E-04
5.332E-04
5.072E-04
4.824E-04
4.539E-04
4.365E-04
4.152E-04
3.950E-04
D-80
-------
Rose Hill, Rl
Table D-20. Southern Parcel Trichloroethene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2034
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+QS
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E405
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-KJ5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-MD5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
2.053E-06
1.953E-06
1.858E-06
1.767E-06
1.6S1E-06
1.599E-06
1.521E-06
1.447E-06
1.376E-06
1.309E-OS
1.245E-06
1.1S5E-06
1.127E-06
1.072E-06
1.020E-06
9.698E-07
9.225E-07
8.775E-07
8.347E-07
7.940E-07
7.553E-07
7.135E-07
6.834E-07
S.501E-07
S.184E-07
5.832E-07
5.595E-07
5.322E-07
5.063E-07
4.816E-07
4.581E-07
4.358E-07
4.145E-07
3.943E-07
3.751E-07
3.568E-07
3.394E-07
3.228E-07
3.071E-07
2.921E-07
2.779E-07
2.643E-07
2.514E-07
2.392E-07
2.275E-07
2.164E-07
2.058E-07
1.958E-07
1.863E-07
1.772E-07
1.685E-07
1.603E-07
1.525E-07
1.451E-07
1.380E-07
1.312E-07
1.248E-07
1.188E-07
1.130E-07
1.075E-07
1.D22E-07
9.723E-08
9.249E-08
8.798E-08
8.369E-08
7.9S1E-08
7.572E-08
7.203E-08
6.852E-08
6.518E-08
6.200E-08
3.757E-04
3.574E-04
3.400E-04
3.234E-04
3.076E-04
2.926E-04
2.733E-04
2.648E-04
2.518E-04
2.396E-04
2.279E-04
2.168E-04
2.062E-04
1.961E-04
1.866E-04
1.775E-04
1.638E-04
1.S06E-04
1.528E-04
1.453E-04
1.3B2E-04
1.315E-04
1.251E-04
1.190E-04
1.132E-04
1.076E-04
1.024E-04
9.740E-05
9.265E-05
8.813E-05
8.383E-05
7.974E-05
7.536E-05
7.216E-05
6.864E-05
6.529E-05
6-211E-Q5
5.908E-05
5 . 620E-05
5.345E-05
5.085E-05
4.337E-05
4.601E-05
4.376E-05
4.163E-05
3.960E-05
3.767E-05
3.533E-05
3.408E-05
3.242E-05
3.034E-05
2.934E-05
2.791E-05
2.654E-Q5
2.525E-05
2.402E-05
2.285E-05
2.173E-05
2.067E-05
1.966E-05
1.871E-05
1.779E-05
1.693E-05
1.610E-05
1.531E-05
1.457E-05
1.3B6E-05
1 . 318E-05
1.254E-05
1.193E-05
1.135E-05
D-81
-------
A Case Study
Table D-20. Southern Parcel Trichloroethene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2131
2182
2183
2184
2185
2136
2137
2188
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+05
977E+05
977E+Q5
977E+OS
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+Q5
977E-1-05
977E+Q5
977E+05
977E+OS
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-K05
977E+05
977E+05
5.
5.
5.
5.
4.
4.
4.
4.
3.
3,
3.
3.
3.
3.
2.
2.
2.
2.
2.
2,
2.
2.
1,
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7,
7 .
7.
6.
6.
6.
5.
897E-OB
610E-08
336E-08
076E-08
828E-03
S93E-08
369E-03
156E-08
953E-08
760E-08
577E-08
403E-08
237E-03
079E-08
929E-08
786E-08
650E-08
S21E-08
398E-03
281E-08
170E-03
064E-08
963E-08
667E-08
776E-08
69QE-08
6Q7E-08
529E-03
454E-08
383E-08
316E-08
252E-03
191E-03
133E-08
077E-08
025E-08
748E-09
273E-09
821E-09
390E-09
981E-09
592E-09
222E-09
870E-09
535E-09
216E-09
913E-09
1
1
9
9
S
8
1
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
. 079E-05
.027E-05
. 765E-06
-239E-06
. 836E-06
, 405E-06
. 995E-06
, 605E-06
.234E-06
.881E-06
. 546E-06
-227E-06
. 923E-06
. 634E-06
. 359E-06
.098E-06
. 849E-06
. 613E-06
.388E-06
, 174E-06
. 970E-06
. 777E-06
. 592E-06
. 417E-06
.251E-06
. Q92E-06
. 941E-06
. 798E-06
. 661E-06
. 532E-06
, 408E-06
-291E-06
. 179E-06
. 073E-06
. 972E-06
. 875E-06
, 784E-06
. 697E-06
. 614E-06
. 535E-06
.461E-06
. 339E-06
.322E-06
.257E-06
. 196E-06
. 137E-06
. 082E-06
D-82
-------
Rose Hill, Rl
Table D-21. Southern Parcel Vinyl Chloride Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 1 volume
Carbon Dioxide : 41.0000 % volume
Air Pollutant : Vinyl Chloride (HAP/VOC)
Molecular wt - 62.50 Concentration - 0-300000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2002
1223S.07 Mg/year
Model Results
Year
Refuse In Place {Mg)
Vinyl Chloride (HAP/VOC) Emission Rate
(Mg/yr) (Cubic tn/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 31SE+04
. 636E+04
.954E+04
.272E+Q4
, 59QE+04
. 908E+04
.226E+04
. Q54E+05
. 186E+05
.318E+05
.450E+05
.5S2E+05
. 713E+05
.845E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
-977E+05
1.
2.
4.
5.
6,
7.
S.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
S.
7.
7.
7 .
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
3.
3.
3.
481E-04
839E-04
229E-04
504E-04
716E-04
869E-04
966E-04
OQ1E-03
100E-03
195E-03
284E-03
370E-03
451E-03
528E-03
602E-03
524E-03
450E-03
379E-03
312E-03
248E-03
187E-03
129E-03
074E-03
021E-03
717E-04
243E-04
792E-04
363E-04
955E-04
567E-04
198E-04
847E-04
513E-04
196E-04
893E-04
606E-04
333E-04
072E-04
825E-04
590E-04
366E-04
153E-04
950E-04
758E-04
575E-04
5
1
1
2
2
3
3
3
4
4
4
5
5
5
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
. 696E-02
. 111E-01
. 627E-01
. 117E-01
-584E-01
.027E-01
. 449E-01
. S51E-01
-232E-01
.596E-01
. 941E-01
.270E-01
.582E-01
. 380E-01
.163E-01
. 862E-01
.576E-01
.304E-01
-045E-01
. 799E-01
-565E-01
.343E-01
-131E-01
. 929E-01
.738E-01
. 555E-01
-382E-01
.217E-01
-060E-01
. 911E-01
. 769E-01
. 634E-01
.506E-01
.383E-01
-267E-01
.157E-01
. 051E-01
. 951E-01
.856E-01
. 766E-01
.679E-01
.59BE-01
-520E-01
, 446E-01
-375E-01
D-83
-------
A Case Study
Table D-21. Southern Parcel Vinyl Chloride Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Kg)
(Mg/yr)
[Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2026
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2080
2081
2082
2033
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E-I-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-1-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-KJ5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-K05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-J-05
1.977E+05
1.977E+05
1.977E+05
3.400E-04
3.234E-04
3.077E-04
2.927E-04
2.784E-04
2.64SE-04
2.519E-04
2.396E-04
2.279E-04
2.168E-04
2.062E-04
1.962E-04
1.866E-04
1.775E-04
1.6B8E-04
1.606E-04
1.528E-04
1.453E-04
1.382E-04
1.315E-04
1.251E-04
1.190E-04
1.132E-04
1.077E-04
1.024E-04
9.742E-05
9.267E-05
B.815E-05
8.385E-05
7.976E-05
7.537E-05
7.217E-05
6.8S5E-05
6.530E-05
6.212E-05
5.909E-05
5.620E-05
5.346E-05
5.D86E-05
4.838E-05
4.602E-05
4.377E-05
4.164E-05
3.9S1E-05
3.7S8E-05
3.584E-05
3.409E-05
3.243E-05
3.035E-05
2.934E-05
2.791E-05
2.655E-05
2.525E-05
2.402E-05
2.235E-05
2.174E-05
2.068E-05
1.967E-05
1.871E-05
1.7BOE-05
1.693E-05
1.610E-05
1.532E-05
1.457E-05
1.3BSE-05
1.318E-05
1.254E-05
1.193E-05
1.135E-05
1.079E-05
1.027E-05
1.308E-01
1.244E-01
1.184E-01
1-126E-01
1.071E-01
1.019E-01
9.690E-02
9.217E-02
8.768E-02
8.340E-02
7.933E-02
7.546E-02
7.178E-02
6.828E-02
S.495E-02
6.179E-02
5.377E-02
5.591E-02
5.318E-02
5.059E-02
4.812E-02
4.577E-02
4.354E-02
4.142E-02
3-940E-02
3.747E-02
3.565E-02
3.391E-02
3.225E-02
3.068E-02
2.919E-02
2.776E-02
2.641E-02
2.512E-02
2.339E-02
2.273E-02
2.162E-02
2.057E-02
1.956E-02
1.861E-02
1.770E-02
1.634E-02
1.602E-02
1.524E-02
1.449E-02
1.379E-02
1.311E-02
1.247E-02
1.137E-02
1.129E-02
1.074E-02
1.021E-02
9.715E-03
9.241E-03
8.790E-03
8.362E-03
7.954E-03
7.566E-03
7.197E-03
6.846E-03
6.512E-03
6.194E-03
5.392E-03
5.605E-03
5.332E-03
5.072E-03
4.324E-03
4.589E-03
4.365E-03
4.152E-03
3.950E-03
D-84
-------
Rose Hill, Rl
Table D-21. Southern Parcel Vinyl Chloride Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place {Mg)
(Mg/yr)
(Cubic m/yr)
2084
2085
2086
2087
2088
2039
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1,
1,
1.
1.
1,
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1,
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-1-05
977E+05
977E+05
977E+05
977E+05
977E+OS
977Et05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+OS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
9.
9.
8.
8.
7.
7.
7.
6,
6.
6.
5.
5.
5.
5.
4.
4,
4.
4.
3.
3.
3.
3.
3,
3.
2.
2.
2.
2.
2.
2,
2,
2.
1.
1,
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
9.
9.
e.
8.
8.
7.
7.
6,
6.
6.
5.
5.
5.
5.
4.
4,
4.
4.
3.
3,
3.
3.
3,
3.
2.
767E-06
291E-06
837E-06
406E-06
996E-06
606E-06
235E-06
883E-06
547E-06
228E-06
924E-06
635E-06
360E-06
099E-06
850E-06
614E-06
339E-06
175E-06
971E-06
777E-06
S93E-06
418E-06
251E-06
093E-06
942E-06
798E-06
662E-06
532E-06
408E-06
291E-06
179E-06
073E-06
972E-06
876E-06
784E-06
697E-06
614E-06
536E-06
461E-06
390E-06
322E-06
257E-Q6
196E-06
138E-06
082E-06
029E-06
792E-07
315E-07
860E-07
428E-07
017E-07
62SE-07
254E-07
900E-07
564E-07
244E-07
939E-07
650E-07
374E-07
112E-07
863E-07
625E-07
400E-07
185E-07
981E-07
787E-07
602E-07
427E-07
260E-07
101E-07
949E-07
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
.757E-03
.574E-03
-400E-Q3
.234E-03
.076E-03
.926E-03
.783E-03
.648E-03
.518E-03
.396E-03
-279E-03
.168E-03
.062E-03
-961E-Q3
.866E-03
.775E-03
.63BE-03
. 606E-03
.528E-03
.453E-03
-382E-03
-315E-03
-251E-03
.190E-03
.132E-03
.076E-03
.024E-03
.740E-04
-265E-04
.813E-04
.333E-04
-974E-Q4
.586E-04
-216E-04
.864E-04
-529E-04
.211E-04
.908E-04
-620E-04
.345E-04
-085E-04
.837E-04
. 601E-04
.376E-04
.163E-04
. 960E-04
-767E-04
.583E-04
.408E-04
-242E-04
.OS4E-04
-934E-04
.791E-04
. 654E-04
.525E-04
.402E-04
-285E-04
.173E-04
-067E-04
.966E-04
.871E-04
.779E-04
.693E-04
.610E-04
.531E-04
-457E-04
.386E-04
.318E-04
•254E-04
-193E-04
.135E-04
D-85
-------
A Case Study
Table D-21. Southern Parcel Vinyl Chloride Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
[Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2163
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
21B1
2132
2183
21B4
2185
2136
2187
21B8
21B9
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+OS
1.977E+-05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+QS
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-1-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
2.806E-07
2.669E-07
2.539E-07
2.415E-07
2.297E-07
2.185E-07
2.076E-07
1.977E-07
1.881E-07
1.739E-07
1.7Q2E-07
1.619E-07
1.540E-07
1.465E-07
1.393E-07
1.325E-07
1.261E-07
1.199E-07
1.141E-07
1.085E-07
1.032E-07
9.818E-08
9.339E-08
8.833E-OS
8.450E-08
S.038E-06
7.646E-08
7.273E-OB
6.918E-08
6.5B1E-08
6.260E-08
5.955E-OS
5.664E-08
5.3B8E-Q8
5.125E-08
4.875E-08
4.63TE-08
4.411E-06
4.196E-08
3.992E-08
3.797E-OB
3.612E-OS
3.436E-08
3.268E-OB
3.109E-08
2.957E-08
2.813E-08
1.079E-04
1.027E-04
9.765E-05
9.239E-05
8.936E-05
8.405E-05
7.995E-05
7.605E-05
7.234E-05
6.331E-05
6.546E-05
6.227E-05
5.923E-05
5.634E-05
5 . 35 9E-05
5.098E-05
4.349E-05
4.613E-05
4.388E-05
4.174E-05
3.970E-05
3.777E-05
3.592E-05
3.417E-05
3.251E-05
3.092E-05
2.941E-05
2.798E-05
2.661E-05
2.532E-05
2.408E-05
2.291E-05
2.179E-05
2.073E-05
1.972E-05
1.375E-05
1.784E-05
1.697E-05
1.614E-05
1.535E-05
1,461E~05
1.339E-05
1.322E-05
1.257E-05
1.196E-05
1.137E-05
1.082E-05
D-86
-------
Rose Hill, Rl
Table D-22. Southern Parcel m,p-Xylene Emisson Rate from Year 1968 to 2203.
Source: H:\3000\030177~1.000X030177-1,002\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo : 170,00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC ; 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 1 volume
Carbon Dioxide : 41.0000 % volume
Air Pollutant : m,p-Xylene (HAP/VOC)
Molecular wt - 106.17 Concentration - 3-750000 ppmv
Landfill Parameters
Landfill type : Co—Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2002
1223S.07 Mg/year
Model Results
Year
Refuse In Place {Mg)
m,p-Xylene (HAP/VQC) Emission Rate
(Mg/yr) (Cubic tti/yr)
196S
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1930
1981
1982
1933
1984
1985
1986
1987
1988
1939
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 31SE+04
. 636E+04
.954E+04
.272E+Q4
, 590E+04
. 908E+04
.226E+04
. Q54E+05
. 186E+05
.318E+Q5
.450E+05
.5S2E+05
. 713E+05
.845E+05
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+Q5
. 977E+Q5
. 977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+OS
. 977E+05
-977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
, 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
-977E-1-05
, 977E+05
-977E+05
3.
6.
8,
1.
1.
1.
1.
2.
2.
2.
2.
2.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2,
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
7 .
7.
144E-03
135E-03
980E-03
169E-02
426E-02
671E-02
904E-02
125E-02
336E-02
537E-02
727E-02
909E-02
081E-02
246E-02
402E-02
236E-02
078E-02
928 E- 02
785E-02
649E-02
S20E-02
397E-Q2
280E-02
169E-02
063E-02
9S3E-02
867E-02
776E-02
689E-02
607E-02
S28E-02
454E-02
333E-02
316E-02
251E-02
190E-02
132E-02
077E-02
025E-02
746E-03
271E-03
81BE-03
388E-03
979E-03
590E-03
7
1
2
2
3
3
4
4
5
5
6
6
6
7
7
7
6
6
6
5
5
5
5
4
4
4
4
4
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
. 120E-01
.339E+00
. 034E+00
. 646E+00
-229E+QO
.784E+00
.311E+00
. 313E+00
-290E+00
.744E+00
-176E+00
.587E+00
. 978E+00
.350E+00
.703E+00
.327E+00
. 970E+00
. 630E+00
-307E+00
. 999E+00
-707E+00
. 428E+00
-164E+00
. 912E+00
. 672E+00
. 444E+00
-228E+00
. 021E+00
-825E+00
. 639E+-00
, 461E+00
.292E+00
.132E+00
. 979E+00
. 834E+00
. 696E+00
. 564E+00
. 439E+00
.320E+00
.207E+00
. 099E+00
. 997E+00
- 900E+00
, 807E+00
. 719E+00
D-87
-------
A Case Study
Table D-22. Southern Parcel m,p-Xylene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-S-05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
7.220E-03
6.868E-03
6.533E-03
6.214E-03
5.911E-03
5-623E-Q3
5.349E-03
5.088E-03
4.840E-03
4.604E-03
4.379E-03
4.166E-03
3.962E-03
3.769E-03
3.535E-03
3.410E-03
3.244E-03
3.086E-03
2. 935 E- 03
2.792E-03
2.656E-03
2.527E-03
2.403E-03
2.286E-03
2.175E-03
2.069E-03
1.968E-03
1.872E-03
1.780E-03
1.694E-03
1.611E-03
1.532E-03
1.458E-03
1.337E-03
1.319E-03
1.255E-03
1.193E-03
1.135E-03
1.080E-03
1.027E-03
9.771E-04
9.295E-04
8.841E-04
8.410E-04
8.000E-04
7.610E-04
7-239E-04
S.886E-04
6.550E-04
6.230E-04
5.926E-04
5.637E-04
5-363E-04
5.101E-04
4.852E-04
4.616E-04
4.390E-04
4.176E-04
3.973E-04
3.779E-04
3-59SE-04
3.419E-04
3-253E-04
3.094E-04
2.943E-04
2.799E-04
2.663E-04
2.533E-04
2.410E-04
2.292E-04
2.180E-04
1.635E+00
1.555E+00
1.479E+00
1.407E+00
1.339E+00
1.273E+00
1.211E+00
1.152E+00
1.096E+00
1.043E-I-00
9.917E-01
9.433E-01
8.973E-01
8.535E-01
8.119E-01
7.723E-01
7.346E-01
6.988E-01
6.647E-01
6.323E-01
6.015E-01
5 . 721E-01
5.442E-01
5.177E-01
4.924E-01
4.684E-01
4.456E-01
4.239E-01
4.032E-01
3.835E-01
3.648E-01
3.470E-01
3.301E-01
3.140E-Q1
2.987E-01
2.841E-01
2.703E-01
2.571E-01
2.445E-01
2.326E-01
2.213E-01
2.105E-01
2.002E-01
1.904E-01
1,812E-01
1.723E-01
1.639E-01
1.559E-01
1.483E-01
1.411E-01
1.342E-01
1.277E-01
1.214E-01
1.155E-01
1.099E-01
1.045E-01
9.942E-02
9.457E-02
8.996E-02
3.557E-02
8.140E-02
7.743E-02
7.365E-02
7.006E-02
6.665E-02
6.340E-02
6.030E-02
5.736E-02
5.456E-02
5.190E-02
4.937E-02
D-88
-------
Rose Hill, Rl
Table D-22. Southern Parcel m,p-Xylene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2034
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+QS
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E405
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E-KJ5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E-MD5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
2.074E-04
1.973E-04
1.877E-04
1.735E-04
1.698E-04
1.615E-04
1.536E-04
1.461E-04
1.390E-04
1.322E-04
1.258E-04
1.197E-04
1.138E-04
1.083E-04
1.030E-04
9.796E-05
9.319E-05
8.8S4E-05
8.432E-05
8.021E-05
7 . 629E-05
7.257E-05
6.903E-05
S.567E-05
S.246E-05
5.942E-05
5.652E-05
5.376E-05
5.114E-05
4.865E-05
4 . 628 E- 05
4.402E-05
4.187E-05
3.983E-05
3.789E-05
3.604E-05
3.428E-05
3.261E-05
3.102E-05
2.951E-05
2.807E-05
2.670E-05
2.S40E-05
2.416E-05
2.298E-05
2.196E-05
2.079E-05
1.97BE-05
1.881E-05
1.790E-05
1.702E-05
1.619E-05
1.540E-05
1.465E-05
1.394E-05
1.326E-05
1.261E-05
1.200E-05
1.141E-05
1.0S5E-05
1.033E-05
9.822E-06
9.343E-06
8.887E-06
8.454E-06
8.041E-06
7.649E-06
7.276E-06
6.921E-06
6.584E-06
6.2S3E-06
4.696E-02
4.467E-02
4.250E-02
4.042E-Q2
3.S45E-02
3.658E-02
3.479E-02
3.310E-02
3.148E-02
2.995E-02
2.849E-02
2.710E-02
2.577E-02
2.452E-02
2.332E-02
2.218E-02
2.110E-02
2.007E-02
1.909E-02
1.816E-02
1.726E-02
1.643E-02
1.563E-02
1.487E-02
1.415E-02
1.346E-02
1.280E-02
1.218E-02
1.158E-02
1.102E-02
1.048E-02
9.968E-03
9.482E-03
9.020E-03
8.580E-03
8.161E-03
7.763E-03
7.385E-03
7.024E-03
6.632E-03
6.356E-03
6.046E-03
5.751E-03
5.471E-03
5.204E-03
4.950E-03
4.709E-03
4.479E-03
4.261E-03
4.053E-03
3.855E-03
3.667E-03
3.488E-03
3.31SE-03
3.156E-03
3.002E-03
2.856E-03
2.717E-03
2.584E-03
2.458E-03
2.338E-03
2.224E-03
2.116E-03
2.013E-03
1.914E-03
1.321E-03
1.732E-03
1.64BE-03
1.567E-03
1.491E-03
1.418E-03
D-89
-------
A Case Study
Table D-22. Southern Parcel m,p-Xylene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-J-05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+05
977E+05
977E+05
977E+05
977E+05
5.
5.
5.
5.
4.
4-
4.
4.
3.
3.
3.
3.
3.
3.
2.
2.
2.
2,
2.
2,
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
8.
8.
8.
7 .
7.
6.
6.
6.
b.
957E-06
667E-06
390E-06
127E-06
877E-06
639E-06
413E-06
198E-06
993E-Q6
798E-06
613E-06
437E-06
269E-06
110E-06
958E-06
814E-06
677E-06
546E-06
422E-06
304E-06
192E-06
085E-06
983E-06
886E-06
794E-06
7Q7E-06
624 E- 06
544E-06
469E-06
397E-06
329E-06
264E-06
203E-06
144E-06
088E-06
035E-06
847E-07
367E-07
910E-07
476E-07
062E-07
669E-07
295E-07
939E-07
601E-07
279E-07
973E-07
1
1
1
1
1
1
9
9
9
a
8
7
7
7
6
6
6
5
5
5
4
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
.349E-03
.283E-Q3
.221E-03
.161E-03
.104E-03
-051E-03
. 994E-04
-506E-04
. 043E-04
. 602E-04
. 182E-04
. 783E-04
.404E-04
-043E-04
. 699E-04
.372E-04
-062E-04
-766E-04
. 485E-04
-217E-04
. 963E-04
.721E-04
, 491E-04
-272E-04
.063E-04
.865E-04
. 677E-04
. 497E-04
-327E-04
.164E-04
.010E-04
. 863E-04
.724E-04
.591E-Q4
-464E-04
.344E-04
-230E-04
.121E-04
.018E-04
. 919E-04
.826E-04
. 737E-04
.652E-04
.571E-04
.495E-04
.422E-04
-353E-04
D-90
-------
Rose Hill, Rl
Table D-23. Southern Parcel o-Xylene Emisson Rate from Year 1968 to 2203.
Source: H:\3000V030177~1.000\030177~1.OD2\ROSEHI~1\SOUTHERN.PRM
Model Parameters
Lo s 170.00 m"3 / Mg ***** user Mode Selection *****
k : 0.0500 1/yr ***** User Mode Selection *****
NMOC : 2550.00 ppmv ***** user Mode Selection *****
Methane : 59.0000 $ volume
Carbon Dioxide : 41.0000 % volume
Air Pollutant : o-Xylene (HAP/VOC)
Molecular wt - 106.17 Concentration - 1.540000 ppmV
Landfill Parameters
Landfill type : Co-Disposal
Year Opened : 1967 Current Year
Capacity : 197692 Mg
Average Acceptance Rate Required from
Current Year to Closure Year
2003 Closure Year: 2002
12238.07 Mg/year
Model Results
Year
Refuse In Place (Mg)
o-Xylene (HAP/VOC) Emission Rate
(Mg/yr) (Cubic m/yr)
1968
1969
1970
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1931
1982
1933
1984
19S5
1936
1987
1988
19B9
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
1
2
3
5
6
7
9
I
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
. 318E+04
. 636E+Q4
. 954E+04
.272E+04
.590E+04
. 9Q8E+04
.226E+04
. 054E+05
. 186E+05
. 318E+05
.450E+05
.582E+05
. 713E+05
.B45E+05
. 977E+Q5
. 977E+Q5
.977E+05
. 977E+05
.977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
.977E+05
. 977E+05
-977E+05
, 977E+05
-977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
-977E+05
-977E+05
. 977E+05
-977E+05
. 977E+05
. 977E+05
. 977E+05
. 977E+05
1.
2.
3.
4.
5.
6.
7.
S.
9.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
9.
9.
S.
8.
8.
1 .
7.
6.
6.
6.
5.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
291E-03
519E-03
68 8 E- 03
799E-03
856E-03
862E-03
819E-03
729E-03
594E-03
042E-02
120E-02
195E-02
265E-02
333E-02
397E-02
329E-02
264E-02
202E-02
144E-02
088E-02
035E-02
844E-03
3S4E-03
907E-03
473E-03
060E-03
667E-03
293E-03
937E-03
599E-03
277E-03
971E-03
680E-03
403E-03
139E-03
888E-03
650E-03
423E-03
208E-03
002E-03
807E-03
621E-03
445E-03
277E-03
117E-03
2
5
S
1
1
1
1
1
2
2
2
2
2
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
. 924E-01
.706E-01
.351E-01
.087E+00
. 326E+00
. 554E+00
. 771E+00
. 977E+00
-173E+QO
.359E+00
.536E+00
-705E+00
. 866E+00
. 018E+00
. 163E+00
.009E+00
. 862E+00
.723E+00
-590E+00
. 464E+00
-344E+00
.229E+00
.121E+00
. 017E+00
. 919E+00
.825E+00
.736E+00
. 651E+-00
-571E+00
.494E+00
. 421E+00
.352E+00
.286E+QO
.223E+00
.164E+00
.107E+00
.053E+00
. 002E+00
-528E-01
. 063E-01
. 621E-01
.201E-01
-801E-Q1
-420E-01
-059E-01
D-91
-------
A Case Study
Table D-23. Southern Parcel o-Xylene Emisson Rate from Year 1968 to 2203 (continued).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic rn/yr)
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
204S
2047
2048
2049
2050
2051
2052
2053
2054
2055
2056
2057
2058
2059
2060
2061
2062
2063
2064
2065
2066
2067
2068
2069
2070
2071
2072
2073
2074
2075
2076
2077
2078
2079
2030
2081
2082
2083
1.977E+Q5
1.977E+Q5
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+OS
1.977E+05
1.977E+05
1.977E+05
1.977E+Q5
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
1.977E+05
2.965E-03
2.820E-03
2.633E-03
2.S52E-03
2.428E-03
2-3Q9E-Q3
2.197E-03
2.0S9E-03
1.9B7E-03
1.891E-03
1.798E-03
1.711E-03
1.627E-03
1.548E-03
1.472E-03
1.401E-03
1.332E-03
1.2S7E-03
1.205E-03
1.147E-03
1.091E-03
1.038E-03
9.870E-04
9.388E-04
8.930E-04
8.495E-04
8.0S1E-04
7.636E-04
7.312E-04
6.955E-04
6.616E-04
6.293E-04
5.986E-04
5.694E-04
5.417E-04
5.152E-04
4.901E-04
4.662E-04
4.435E-04
4.21SE-04
4.013E-04
3.817E-04
3.631E-04
3.454E-04
3.285E-04
3.125E-04
2-973E-04
2.82SE-04
2.690E-04
2.559E-04
2.434E-04
2.315E-04
2-202E-04
2.095E-04
1.993E-04
1.895E-04
1.803E-04
1.715E-04
1.631E-04
1.552E-04
1.476E-04
1.404E-04
1.336E-04
1.271E-04
1.209E-04
1.150E-04
1.094E-04
1.040E-04
9.895E-05
9.413E-05
8-953E-05
6.714E-01
6.387E-01
6.075E-01
5.779E-01
5.497E-01
5.229E-01
4.974E-Q1
4.732E-01
4.501E-01
4.281E-01
4.072E-01
3-874E-01
3.685E-01
3.505E-01
3.334E-01
3.172E-01
3.017E-01
2.870E-01
2.730E-01
2.597E-01
2.470E-01
2.350E-01
2.235E-01
2.126E-01
2.022E-01
1.924E-01
1.830E-01
1.741E-01
1.656E-01
1.575E-01
1.498E-01
1.425E-01
1.356E-01
1.239E-Q1
1.227E-01
1.167E-01
1.110E-01
1.056E-01
1.004E-01
9.553E-02
9.087E-02
8.644E-02
8.222E-02
7.321E-02
7.440E-02
7.077E-02
6.732E-02
6.403E-02
6.091E-02
5.794E-02
5.511E-02
5.243E-02
4.987E-02
4.744E-02
4.512E-02
4.292E-02
4.083E-02
3.834E-02
3.694E-02
3.514E-02
3.343E-02
3.130E-Q2
3.025E-02
2.877E-02
2.737E-02
2.603E-02
2.476E-02
2.356E-02
2.241E-02
2.132E-02
2.028E-02
D-92
-------
Rose Hill, Rl
Table D-23. Southern Parcel o-Xylene Emisson Rate from Year 1968 to 2203 (continued).
Year
Re/use In Place (Mg)
CMg/yr)
(Cubic m/yr)
2034
2085
2036
2037
2038
2089
2090
2091
2092
2093
2094
2095
2096
2097
2098
2099
2100
2101
2102
2103
2104
2105
2106
2107
2108
2109
2110
2111
2112
2113
2114
2115
2116
2117
2118
2119
2120
2121
2122
2123
2124
2125
2126
2127
2128
2129
2130
2131
2132
2133
2134
2135
2136
2137
2138
2139
2140
2141
2142
2143
2144
2145
2146
2147
2148
2149
2150
2151
2152
2153
2154
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
I,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1,
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+QS
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E405
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
8.
8.
7.
7.
6.
6-
6.
6,
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
9.
9.
8.
8.
8.
7.
7.
6.
6.
6.
6.
5.
5.
5.
4.
4.
4.
4,
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
517E-05
1Q1E-OS
7Q6E-05
331E-05
973E-05
633E-05
309E-05
002E-05
709E-Q5
431E-05
166E-05
914E-05
674E-05
446E-05
229E-05
023E-05
827E-05
640E-05
463E-05
294E-05
133E-05
930E-05
835E-05
697E-05
565E-05
440E-05
321E-05
208E-05
100E-05
998E-05
900E-05
8Q8E-05
720E-05
636E-05
556E-05
430E-05
408E-05
339E-05
274E-05
212E-05
153E-05
096E-05
043E-05
92 IE- 06
437E-06
977E-06
S39E-06
122E-06
726E-06
349E-06
991E-06
650E-06
326E-06
017E-06
724E-06
445E-Q6
179E-06
927 E- 06
686E-06
458E-06
240E-06
033E-06
837E-06
650E-06
472E-06
302E-06
141E-06
9B8E-06
842E-06
704E-06
572E-06
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
. 929E-02
.835E-Q2
. 745E-02
, 660E-Q2
.579E-02
-502E-02
. 429E-02
-359E-02
.293E-02
.230E-02
. 170E-02
-113E-02
.058E-02
-007E-02
.577E-03
.110E-03
-666E-03
-243E-03
. 341E-03
-459E-03
. 095E-03
.749E-03
, 420E-03
-107E-03
.809E-03
.526E-03
.256E-03
. OQOE-03
-756E-03
.524E-03
.303E-03
. 094E-03
. 394E-03
. 704E-03
-523E-03
.352E-03
. 188E-03
-033E-03
.385E-03
. 744E-03
.610E-03
. 433E-03
.362E-03
.247E-03
.137E-03
.033E-03
. 934E-03
. B39E-03
-750E-Q3
. 664E-03
-583E-03
.506E-03
-432E-03
.363E-03
-296E-03
.233E-03
-173E-03
.116E-03
-Q61E-03
. 009E-03
-602E-04
. 134E-04
. 689E-04
-265E-04
.862E-04
. 478E-04
.114E-04
. 767E-04
-437E-04
-123E-04
. 824E-04
D-93
-------
A Case Study
Table D-23. Southern Parcel o-Xylene Emisson Rate from Year 1968 to 2203 (concluded).
Year
Refuse In Place (Mg)
(Mg/yr)
(Cubic m/yr)
2155
2156
2157
2158
2159
2160
2161
2162
2163
2164
2165
2166
2167
2168
2169
2170
2171
2172
2173
2174
2175
2176
2177
2178
2179
2180
2181
2182
2183
2184
2185
2186
2187
21B8
2189
2190
2191
2192
2193
2194
2195
2196
2197
2198
2199
2200
2201
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
I.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1.
1.
1.
1.
1.
1.
1.
977E+Q5
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E-J-05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+Q5
977E+05
977E+05
977E+05
977E+05
977E+05
977E+05
977E+-05
977E+05
977E+05
977E+05
977E+05
977E+05
2.
2.
2.
2.
2.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
9.
9^.
9.
8.
8.
7.
7 .
7.
6.
6.
6.
5.
5.
5.
4.
4.
4.
4.
4.
3.
3.
3.
3.
3.
2.
2.
2.
2.
2-
446E-06
327E-06
214E-06
106E-06
003E-06
905E-06
812E-06
724E-06
640E-Q6
560E-06
484E-06
411E-06
343E-06
277E-06
215E-06
156E-06
099E-06
046E-06
946E-07
461E-07
OOOE-07
561E-07
143E-07
746E-07
369E-07
009E-07
667E-07
342E-07
033E-07
739E-07
459E-07
192E-07
939E-07
698E-07
469E-07
251E-07
044E-07
847E-07
659E-07
4B1E-Q7
311E-07
149E-Q7
996E-07
850E-07
711E-07
579E-07
453E-07
5
5
5
4
4
4
4
3
3
3
3
3
3
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
9
9
8
8
7
7
7
6
6
6
5
5
.540E-04
.27QE-Q4
, 013E-04
. 768E-04
.536E-04
-315E-04
. 104E-04
-904E-04
. 714E-04
.532E-04
-360E-04
-196E-04
.040E-04
-892E-04
.751E-04
.617E-04
-489E-04
-368E-04
.252E-04
-143E-04
. 036E-04
. 939E-04
, 844E-04
-7S4E-04
. 669E-04
.587E-04
.510E-04
. 436E-04
.366E-04
.300E-04
.236E-04
. 176E-04
. 119E-04
. 064E-Q4
-012E-04
. 627E-05
. 158E-05
-711E-05
.286E-05
. S32E-05
.498E-05
. 132E-05
.784E-05
. 453E-05
.139E-05
.839E-05
-554E-OS
D-94
-------
Rose Hill, Rl
Appendix E
SCREEN3 Model Runs
E-l
-------
A Case Study
*** SCREEN3 MODEL RUN ***
*** VERSION DATED 96043 ***
Rose Hill Northern Portion
SIMPLE TERRAIN INPUTS:
SOURCE TYPE
EMISSION RATE (G/(S-M**2))
SOURCE HEIGHT (M)
LENGTH OF LARGER SIDE {M)
LENGTH OF SMALLER SIDE (M)
RECEPTOR HEIGHT (M)
URBAN/RURAL OPTION
02/20/03
09:27:30
AREA
0.158730E-04
0.0000
300.0000
210.0000
0.0000
RURAL
THE REGULATORY (DEFAULT) MIXING HEIGHT OPTION WAS SELECTED.
THE REGULATORY (DEFAULT) ANEMOMETER HEIGHT OF 10.0 METERS WAS ENTERED.
MODEL ESTIMATES DIRECTION TO MAX CONCENTRATION
BUOY. FLUX = 0.000 M**4/S**3; MOM. FLUX
*+* FULL METEOROLOGY ***
**********************************
*** SCREEN AUTOMATED DISTANCES ***
0.000 M**4/S**2.
TERRAIN HEIGHT OF
0. M ABOVE STACK BASE USED FOR FOLLOWING DISTANCES *:
DIST
(M)
1.
100.
200.
300.
400.
500.
600.
700.
800.
900.
1000.
1100.
1200.
1300.
1400.
1500.
1600.
1700.
1800.
1900.
2000.
2100.
2200.
CONG
(UG/M**3)
2024
2303
162<3
878.
653.
529.
447.
389.
347.
314.
288.
266.
248.
232.
218.
205.
194.
184.
174.
166.
158.
151.
145.
.
.
.
5
7
2
4
7
0
5
2
6
3
4
3
8
5
3
9
4
6
6
1
STAB
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
U10M
(M/S)
1
1
1
1
1
1
1
1
1
1
\
I
1
1
1
1
1
1
1
1
1
1
1
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
USTK
(M/S)
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
MIX HT
(M)
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
PLUME MAX D1R
HT (M) (DEG)
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
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
34.
33.
35.
34.
33.
33.
32.
31.
30.
29.
28.
2S.
25.
23.
22.
18.
17.
13.
6.
1.
2.
0.
0.
E-2
-------
Rose Hill, Rl
2300.
2400.
2500.
2600.
2700.
2800.
2900.
3000.
3500.
4000.
4500.
5000.
5500.
6000.
6500.
7000.
7500.
8000.
8500.
9000.
9500.
10000.
15000.
20000.
25000.
30000.
40000.
50000.
MAXIMUM
139.0
133.3
127.9
122.9
118.0
113.5
109.2
105.3
89
76
66
58
52
46
42
38
35
32
30
28
26
24
14
10
8.
6.
4.
3.
1-HR
.11
.59
.70
.73
.23
.88
.36
.55
.42
.68
.29
.21
.37
.71
.74
.46
005
432
628
589
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
1
1
1
1
1
1
1
1
I
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
CONCENTRATION AT
183. 2483.
*** SUMMARY
***********v
CALCULATION
PROCEDURE
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
OR
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
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
BEYOND
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
10000.
1.
6 1.0 1.0 10000.
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
M:
0
OF SCREEN MODEL RESULTS ***
t**********+****************
MAX CONG
(UG/M**3)
DTST
TO
MAX (M)
TERRAIN
HT
(M)
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.
2.
0.
2.
0.
1.
1.
0.
1.
0.
0.
0.
1.
0.
1.
1.
0.
1.
1.
1.
0.
1.
1.
0.
0.
0.
0.
0.
35.
SIMPLE TERRAIN
2483.
183.
0.
E-3
-------
A Case Study
*** SCREEN3 MODEL RUN ***
*** VERSION DATED 96043 ***
Rose Hill Southern Portion
SIMPLE TERRAIN INPUTS:
SOURCE TYPE
EMISSION RATE (G/(S-M**2))
SOURCE HEIGHT (M)
LENGTH OF LARGER SIDE {M)
LENGTH OF SMALLER SIDE (M)
RECEPTOR HEIGHT (M)
URBAN/RURAL OPTION
02/20/03
09:28:31
AREA
0.138890E-04
0.0000
300.0000
240.0000
0.0000
RURAL
THE REGULATORY (DEFAULT) MIXING HEIGHT OPTION WAS SELECTED.
THE REGULATORY (DEFAULT) ANEMOMETER HEIGHT OF 10.0 METERS WAS ENTERED.
MODEL ESTIMATES DIRECTION TO MAX CONCENTRATION
BUOY. FLUX = 0.000 M**4/S**3; MOM. FLUX
*+* FULL METEOROLOGY ***
**********************************
*** SCREEN AUTOMATED DISTANCES ***
0.000 M**4/S**2.
TERRAIN HEIGHT OF
0. M ABOVE STACK BASE USED FOR FOLLOWING DISTANCES *:
DIST
(M)
1.
100.
200.
300.
400.
500.
600.
700.
800.
900.
1000.
1100.
1200.
1300.
1400.
1500.
1600.
1700.
1800.
1900.
2000.
2100.
2200.
CONG
(UG/M**3)
1796
2033
1644
819.
605.
488.
412.
359.
320.
289.
265.
245.
228.
214.
201.
189.
179.
169.
161.
153.
146.
140.
134.
.
.
.
5
2
9
9
5
0
9
7
7
8
2
2
7
3
9
3
5
4
1
4
STAB
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
U10M
(M/S)
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
USTK
(M/S)
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
MIX HT
(M)
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
10000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
PLUME MAX D1R
HT (M) (DEG)
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
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
38.
38.
39.
38.
38.
37.
37.
36.
36.
35.
35.
34.
33.
32.
31.
31.
30.
29.
27.
26.
25.
22.
21.
E-4
-------
Rose Hill, Rl
2300. 129.1
2400. 124.1
2500. 119.4
2600. 115.0
2700. 110.8
2800. 106.9
2900. 103.2
3000. 99.72
3500. 65.33
4000. 73.95
4500. 64.79
5000. 57.31
5500. 51.14
6000. 46.04
6500. 41.68
7000. 38.04
7500. 34.97
8000. 32.31
8500. 30.01
9000. 27.96
9500. 26.13
10000. 24.51
15000. 14.69
20000. 10.43
25000. 8.001
30000. 6.428
40000. 4.625
50000. 3.587
6
6
6
6
6
6
6
6
g
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
MAXIMUM 1-HR CONCENTRATION AT
191. 2191.
*** SUMMARY
***********v
CALCULATION
PROCEDURE
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
1.0 1.0 10000.0
OR BEYOND 1. M:
6 1.0 1.0 10000.0
OF SCREEN MODEL RESULTS ***
t**********+****************
MAX CONG
(UG/M**3)
DTST TO TERRAIN
MAX (M) HT (M)
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
19.
18.
14.
12.
11.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
38,
SIMPLE TERRAIN
2191.
191.
0.
E-5
------- |