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

-------
                                     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

-------
                                          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.

-------
                                            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

-------
                               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

-------
                              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

-------
                                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

-------
                                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

-------
                              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

-------
                                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

-------
                                                                                     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.

-------
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.

-------
A Case Study

-------
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.

-------
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.

-------
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.

-------
A Case Study

-------
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.

-------
                                                                                                 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.

-------
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
    

    -------