Circular Economy
Circular Economy (CircularEconomy) includes three subsectors (* indicates non-emission subsector):
Liquid Waste* (WALI)
Solid Waste (WASO)
Wastewater Treatment (TRWW)
Circular Economy is used to account for the production of, and emissions from, liquid and solid waste from industrial and domestic sources. Circular Economy includes three subsectors: liquid waste (used only to account for the production of liquid waste), solid waste, and wastewater treatment. These three sectors are derived from Volume 5 of the IPCC guidance for national greenhouse gas inventories and include detailed estimates of of emissions from wastewater treatment and management pathways, solid waste treatment pathways, including a first order decay model of landfilled waste, and recycling, which then is passed to the industrial production model to estimate changes to production of virgin materials. Waste generation is primarily driven by per person generation factors, which are responsive to changes in GDP, GDP/capita, and population and other sectors, including livestock manure management and supply chain loss in agriculture.
Liquid Waste (WALI)
Liquid waste includes…
Categories
Categories associated with Liquid Waste are identified by the $CAT-WASTE-LIQUID$ variable schema element and shown in the category attribute table shown below.
Category Name |
|
Description |
Data Source |
Hyperlink |
Notes |
|
Industrial Category |
|---|---|---|---|---|---|---|---|
Industrial Wastewater |
|
Industrial liquid waste, driven by the production of industrial goods |
|
none |
|
||
Rural Domestic Wastewater |
|
Domestic urban wastewater–generally composed of human waste (sewage) and driven by population. Urban populations generally have higher access to sewerage. |
|
|
none |
||
Urban Domestic Wastewater |
|
Domestic urban wastewater–generally composed of human waste (sewage) and driven by population. Urban populations generally have higher access to sewerage. |
|
|
none |
Variables
Variables associated with the Liquid Waste subsector are shown below.
Variable Type |
Variable |
Information |
Variable Schema |
Categories |
Reference |
Default Value |
Default LHS Scalar Minimum at Final Time Period |
Default LHS Scalar Maximum at Final Time Period |
Simplex Group |
Emissions Total by Gas Component |
|
IPCC Emissions Sector Codes |
IPCC Equation Reference |
Notes |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Input |
(Optional) Elasticity of Protein in Diet to GDP per Capita |
Used if run indepedently from the AFOLU model. In the integrated modeling framework, growth in demand per capita for livestock is used to estimate growth in protein contained in diets. However, the model may be run in isolation. In this case, users can use an elasticity in combination with the fraction of the population that does not eat red meat. |
|
none |
0 |
0.8 |
1.2 |
0 |
none |
|||||
Input |
Average Protein Consumption Per Capita |
Daily protein consumption per person in kg |
|
none |
0 |
1.0 |
1.0 |
0 |
none |
Estimated starting with point estimate of 65.7 grams per person per day in 1984 (see Sepulveda (1984)). Then Andreoli et al. (2021) was used to estimate that protein consumption in latin america from animal protein was approximately 27.5 grams per person per day in 1984, which then grew to 37.5 by 2017 (an increase of 10 grams per day). This gives the baseline of 0.0777 kg per person per day. Consumption of vegetable protein in a standard diet is assumed to be constant. |
||||
Input |
BOD Correction Factor for TOW |
Correction factor for average annual BOD per capita that represents sewage from commercial and industrial operations. |
|
none |
0 |
0.8 |
1.2 |
0 |
none |
See I in Equation 6.3 (IPCC GNGHGI V5,C6) |
||||
Input |
BOD per Capita |
Annual biochemical oxygen demand (BOD) per person in kg. Table 6.4 in IPCC Guidelines for NGHG Inventories shows regional factors. |
|
none |
0 |
0.78 |
1.22 |
0 |
none |
|||||
Input |
COD per GDP |
Average annual chemical oxygen demand (COD) in industrial water per GDP at time \(t = 0\). Mean and range derived from Volume 5, Table 6.9 in IPCC Guidelines for NGHG Inventories. |
|
none |
0 |
0.37 |
2.17 |
0 |
none |
|||||
Input |
Factor for Nitrogen in Non-Consumed Protein Disposed in Sewer System |
\(F_{NON-CON}\) in Equation 6.10 in V5, C6 IPCC GNGHGI (2019R). Default values by region are available in Table 6.10A. |
|
none |
0 |
1.0 |
1.0 |
0 |
none |
See V5, C6, Table 6.10A IPCC GNGHGI |
||||
Input |
Fraction of Protein in Diet with Red Meat |
|
none |
0 |
1.0 |
1.0 |
0 |
none |
Used to estimate protein content in domestic wastewater. Protein (see IPCC GHG Guidance) . See Table 1 in Papier et al. (2019) for the source of these numbers. |
|||||
Input |
Fraction of Protein in Diet without Red Meat |
|
none |
0 |
1.0 |
1.0 |
0 |
none |
||||||
Input |
Initial Per Capita Annual Domestic Wastewater Generated |
Represents the estimated volume, in \(\text{m}^3\)/year, that each person produces in domestic wastewater. This production This value is modified by the log elasticity of production to gdp/capita. Increasing GDP/Capita is associated with increasing per capita liquid waste generation; see Jones, Vliet, Qadir, and Bierkens (2021). |
|
|
0 |
1.0 |
1.0 |
0 |
none |
Default global average of 49 m3/person/year from Jones, Vliet, Qadir, and Bierkens. |
||||
Input |
Initial Per GDP Annual Industrial Wastewater Generated |
Represents the estimated quantity, in m3/year, produced per billion $ GDP. |
|
|
0 |
1.0 |
1.0 |
0 |
none |
|||||
Input |
Log Elasticity DWW Production to GDP Per Capita |
Log elasticity \(\varepsilon\) of domestic wastewater production per capita to GDP/capita. For a year over year growth in GDP/capita \(\Delta g\), the change in domestic wastewater production per capita is estimated as \(\Delta W_{d} = (1 + \Delta g)^{\varepsilon} - 1\). |
|
none |
0 |
0.8 |
1.2 |
0 |
none |
Derived from Jones, Vliet, Qadir, and Bierkens : Country-level and gridded estimates of wastewater production, collection, treatment and reuse, Earth Syst. Sci. Data, 13, 237–254, https://doi.org/10.5194/essd-13-237-2021, 2021. See table 3.1 for the regression coefficient associated with the log production of wastewater, found as 0.31. |
||||
Input |
Maximum BOD \(\text{CH}_4\) Producing Capacity |
\(B_O\) from IPCC Guidelines for NGHG Inventories–or maximum CH4 producing capacity, kg \(\text{CH}_4\)/kg BOD. |
|
none |
0 |
0.8 |
1.2 |
0 |
none |
See V5, C6, Table 6.2 IPCC GNGHGI |
||||
Input |
Maximum COD \(\text{CH}_4\) Producing Capacity |
\(B_O\) from IPCC Guidelines for NGHG Inventories–or maximum CH4 producing capacity, kg \(\text{CH}_4\)/kg COD. |
|
none |
0 |
0.8 |
1.2 |
0 |
none |
See V5, C6, Table 6.2 IPCC GNGHGI |
||||
Input |
Nitrogen Density of Industrial Wastewater |
Nitrogen density of industrial wastewater |
|
|
0 |
0.5 |
2.0 |
0 |
none |
See V5, C6, Table 6.12 IPCC GNGHGI |
||||
Input |
Phosphorous Per BOD Factor |
Ratio of phosphorous to BOD. Unitless. Used in calculating benefits of water treatment |
|
none |
0 |
0.8 |
1.6 |
0 |
none |
|||||
Input |
Phosphorous Per COD Factor |
Ratio of phosphorous to COD. Unitless. Used in calculating benefits of water treatment |
|
none |
0 |
0.8 |
1.6 |
0 |
none |
|||||
Input |
Scalar to Account for Nitrogen in Household Products |
\(N_{HH}\) in Equation 6.10 in V5, C6 IPCC GNGHGI (2019R). Default values by region are available in Table 6.10A. |
|
none |
0 |
1.0 |
1.0 |
0 |
none |
See V5, C6, Table 6.10A IPCC GNGHGI |
||||
Input |
Treatment Fraction Advanced Aerobic |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Treatment Fraction Advanced Anaerobic |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Treatment Fraction Improved Latrine |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Treatment Fraction Primary |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Treatment Fraction Secondary Aerobic |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Treatment Fraction Secondary Anaerobic |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Treatment Fraction Septic |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Treatment Fraction Unimproved Latrine |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Treatment Fraction Untreated No Sewerage |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Treatment Fraction Untreated With Sewerage |
|
all |
0 |
1.0 |
1.0 |
1.0 |
0 |
|
Wastewater Treatment (TRWW)
Wastewater can be treated using a variety of pathways. Note that aerobic and septic pathways produce sludge, which can disposed of in a variety of ways; the SISEPUEDE model does not currently integrate sludge removal and disposal from aerobic and septic treatment pathways.
Note
IPCC accounting (IPCC GNGHGI V5, C6 2019R) calls for emissions from secondary sludge extracted from aerobic WWTPs to be divided between decentralized treatment (uncollected) and centralized treatment, where centralized aerobic treatment includes sludge treatment on-site, accounting for emissions of sludge due to treatment–e.g., from anaerobic decomposition–in the Wastewater Treatment sector. Instead, SISEPUEDE accounts for all emissions from sludge treatment in the Solid Waste sector.
Categories
Categories associated with Wastewater Treatment are identified by the $CAT-WASTEWATER-TREATMENT$ variable schema element and shown in the category attribute table shown below.
Category Name |
|
Description |
Data Source |
Hyperlink |
Notes |
Default TOW Removal Fraction |
Default TOW Removal Fraction Lower Bound |
Default TOW Removal Fraction Upper Bound |
|---|---|---|---|---|---|---|---|---|
Aerobic Treatment - Advanced |
|
|
In aerobic treatment facilities, waste is removed as sludge. |
0.9 |
0.8 |
0.95 |
||
Aerobic Treatment - Secondary |
|
Primary and secondary treatment (mechanical + biological) aerobic wastewater treatment facilities. |
0.85 |
0.8 |
0.9 |
|||
Anaerobic Treatment - Advanced |
|
|
In anaerobic treatment facilities, waste is decomposed anaerobically, creating \(\text{CH}_4\) emissions. |
0.9 |
0.8 |
0.95 |
||
Anaerobic Treatment - Secondary |
|
Primary and secondary treatment (mechanical + biological) anaerobic wastewater treatment facilities. |
0.85 |
0.8 |
0.9 |
|||
Latrines - Improved |
|
Improvemed latrines are assumed to be associated with higher anaerobic decomposition activity, releasing more methane. |
0.6 |
0.4 |
1 |
|||
Latrines - Unimproved |
|
Unimproved latrines |
0.1 |
0.05 |
0.15 |
|||
Primary Treatment |
|
Primary treatment only (mechanical) wastewater treatment facilities. |
0.4 |
0.25 |
0.5 |
|||
Septic |
|
Septic tanks, which are a common treatment option in rural areas. |
In properly managed septic tanks, a fraction of waste is removed as sludge, which is then disposed of in the solid waste stream. |
0.625 |
0.5 |
0.6 |
||
Untreated No Sewerage |
|
Wastewater that is untreated without sewerage. Sewerage reduces methane emissions from anaerobic decomposition. Incudes sea, river, and lake disharge as well as open, stagnant sewers. |
0 |
0 |
0.1 |
|||
Untreated With Sewerage |
|
Wastewater that is sent to sewers (clean, closed, moving), but is not treated afterwards. While there are no \(\text{CH}_4\) emissions from these sewers, effluent contains significant emissions. |
0 |
0 |
0.1 |
Variables
Variables associated with the Wastewater Treatment subsector are shown below.
Variable Type |
Variable |
Information |
Variable Schema |
Categories |
Reference |
Default Value |
Default LHS Scalar Minimum at Final Time Period |
Default LHS Scalar Maximum at Final Time Period |
Simplex Group |
Emissions Total by Gas Component |
IPCC Emissions Sector Codes |
IPCC Equation Reference |
Notes |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Input |
\(\text{K}_{REM}\) Sludge Factor |
Fraction of raw sludge removed from aerboic treatmeant plants |
|
|
0 |
0.46 |
1.39 |
0 |
See V5, C6, Equation 6.3B and Table 6.6A in 2019R IPCC GNGHGI. Increasing this factor can represent investments in upgrades to aerobic treatment (or new facilities). |
||||
Input |
\(\text{N}_2\text{O}\) Wastewater Treatment Emission Factor |
Nitrus oxide emission factor for wastewater treatment as a function of total nitrogen. |
|
all |
0 |
0.8 |
1.2 |
0 |
|
||||
Input |
Biogas Recovery Factor at Wastewater Treatment Plants |
Fraction of biogas recovered from treatment |
|
|
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Fraction of Nitrogen Removed in Treatment |
Wastewater treatment removes some fraction of nitrogen, similar to the methane correction factor. See V5, C6, Equation 6.8 and Tables 6.10B and 6.10C. |
|
all |
0 |
1.0 |
1.0 |
0 |
|
||||
Input |
Fraction of Phosphorous Removed in Treatment |
|
all |
0 |
1.0 |
1.0 |
0 |
|
|||||
Input |
Fraction of Total Organic Waste Removed in Treatment |
|
all |
0 |
0.8 |
1.2 |
0 |
|
|||||
Input |
Septic Sludge Compliance Fraction |
Fraction the population managing their septic tank in compliance with the sludge removal instruction of their septic system |
|
|
0 |
0.5 |
1.5 |
0 |
See V5, C6, Equation 6.3C |
||||
Input |
Wastewater Treatment Methane Correction Factor |
|
all |
0 |
0.8 |
1.2 |
0 |
See Table 6.3 in IPCC Guidelines for NGHG Inventories |
|||||
Output |
\(\text{CH}_4\) Emissions from Wastewater Treatment |
Methane emissions from wastewater treatment |
|
all |
0 |
1.0 |
1.0 |
1 |
|||||
Output |
\(\text{N}_2\text{O}\) Emissions from Wastewater Effluent |
Nitrus oxide emissions from protein content in wastewater. |
|
all |
0 |
1.0 |
1.0 |
1 |
|||||
Output |
\(\text{N}_2\text{O}\) Emissions from Wastewater Treatment |
Nitrus oxide emissions from treatment processes. |
|
all |
0 |
1.0 |
1.0 |
1 |
|||||
Output |
Biogas Recovered from Wastewater Treatment Plants |
|
none |
0 |
1.0 |
1.0 |
0 |
||||||
Output |
Mass of Sludge Produced |
Total mass of sludge produced from wastewater treatment (aerobic and septic treatment pathways) in tonnes |
|
|
0 |
1.0 |
1.0 |
0 |
Total mass of sludge produced, which then is sent to the solid waste model. |
||||
Output |
Total BOD Organic Waste in Effluent |
Total organic waste in effluent released from different pathways from BOD |
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total BOD Removed in Treatment |
Total BOD treated by wastewater treatment type |
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total COD Organic Waste in Effluent |
Total organic waste in effluent released from different pathways from BOD |
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total COD Removed in Treatment |
Total COD treated by wastewater treatment type |
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total Nitrogen Removed in Treatment |
|
none |
0 |
1.0 |
1.0 |
0 |
||||||
Output |
Total Nitrogen in Effluent |
|
none |
0 |
1.0 |
1.0 |
0 |
||||||
Output |
Total Phosphorous Removed in Treatment |
|
none |
0 |
1.0 |
1.0 |
0 |
||||||
Output |
Total Phosphorous in Effluent |
|
none |
0 |
1.0 |
1.0 |
0 |
||||||
Output |
Volume of Wastewater Treated |
|
all |
0 |
1.0 |
1.0 |
0 |
Solid Waste (WASO)
Solid waste is generated by consumption. Growth in domestic consumption in is driven by GDP per capita, while growth in industrial consumption is driven by production (represented by value added). Solid waste can reach one of four final states: incineration (or open-burning), landfilled, recycling (or composting/anaerobic biogas production for food and yard waste).
Note
Process emissions for recycling of recyclable materials that affect virgin production–glass, metals, paper, plastic, rubber and leather, textiles, wood–are treated in Industrial Processes and Product Use.
Categories
Categories associated with Solid Waste are identified by the $CAT-WASTE-SOLID$ variable schema element and shown in the category attribute table shown below.
Note
The solid waste attribute table requires the specification of parameters used to characterize different types of waste. These parameters–with the exception of industrial and chemical waste–are derived from default values provided by the IPCC in Volume 5, Chapter 2, Table 2.4 of the 2019 Refinement to the 2006 IPCC Guidelines for National Greenhouse Gas Inventories and the 2006 IPCC Guidelines for National Greenhouse Gas Inventories (which contains the table) for the source of parameters. Industrial parameters come from Volume 5, Chapter 2, Table 2.5.
Category Name |
|
Description |
Data Source |
Hyperlink |
Notes |
Dry Matter Content as Fraction Wet Weight |
DOC Content as Fraction Wet Waste |
DOC Content as Fraction Dry Waste |
DOCf Degradable |
Total Carbon Content as Fraction Dry Weight |
Fossil Carbon Fraction as Fraction Total Carbon |
Food Category |
Sewage Sludge Category |
|
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Chemical and Industrial |
|
Industrial and chemical solid waste - includes mercury containing devices, computers and electronics, batteries, silica gel, and other chemical solid waste. |
|
0.9 |
0.01 |
0.01 |
0 |
0.5 |
0.9 |
0 |
0 |
none |
||
Food |
|
Food and organic waste, excluding yard and garden waste |
0.4 |
0.15 |
0.38 |
0.7 |
0.38 |
0 |
1 |
0 |
none |
|||
Glass |
|
Glass |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
|||
Metals |
|
Metals |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
|||
Other |
|
Other waste not mentioned in any other category, including sanitary napkins and diapers. |
0.9 |
0 |
0 |
0 |
0.03 |
1 |
0 |
0 |
none |
|||
Paper |
|
Paper products, including cardboard |
0.9 |
0.4 |
0.44 |
0.5 |
0.46 |
0.01 |
0 |
0 |
|
|||
Plastic |
|
Plastic |
1 |
0 |
0 |
0 |
0.75 |
1 |
0 |
0 |
|
|||
Rubber and Leather |
|
Rubber and leather |
Assigned DOCf to less decompostable waste in IPCC FOD model. |
0.84 |
0.39 |
0.47 |
0.1 |
0.67 |
0.2 |
0 |
0 |
|
||
Sanitary Napkins |
|
Sanitary napkins, nappies, diapers |
0.4 |
0.24 |
0.6 |
0.5 |
0.7 |
0.1 |
0 |
0 |
none |
|||
Sludge |
|
Sludge from wastewater |
|
0 |
0.05 |
0.3 |
0.1 |
0.3 |
0 |
0 |
1 |
none |
||
Textiles |
|
Clothing and textiles |
0.8 |
0.24 |
0.3 |
0.5 |
0.5 |
0.2 |
0 |
0 |
|
|||
Wood |
|
Wood and wood products |
0.85 |
0.43 |
0.5 |
0.1 |
0.5 |
0 |
0 |
0 |
|
|||
Yard |
|
Garden and yard waste |
0.4 |
0.2 |
0.49 |
0.4 |
0.49 |
0 |
0 |
0 |
none |
Variables
Variables associated with the Solid Waste subsector are shown below.
Variable Type |
Variable |
Information |
Variable Schema |
Categories |
Reference |
Default Value |
Default LHS Scalar Minimum at Final Time Period |
Default LHS Scalar Maximum at Final Time Period |
Simplex Group |
Emissions Total by Gas Component |
IPCC Emissions Sector Codes |
IPCC Equation Reference |
Notes |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Input |
\(\text{CH}_4\) Anaerobic Biogas Emission Factor |
Emission factor representing fugitive emissions of methane from anaerobic decomposition in biogas facilities. |
|
|
0 |
0.57 |
1.43 |
0 |
Default set as mean between wet and dry weight factors from Volume 5, Table 4.1 in IPCC Guidelines for NGHG Inventories. |
||||
Input |
\(\text{CH}_4\) Composting Emission Factor |
Emission factor representing emissions of methane from composting of organic materials |
|
|
0 |
0.57 |
1.43 |
0 |
Default set as mean between wet and dry weight factors from Volume 5, Table 4.1 in IPCC Guidelines for NGHG Inventories. |
||||
Input |
\(\text{CH}_4\) ISW Incineration Emission Factor |
Based on IPCC Tier 1 approach–\(\text{CH}_4\) emissions from incineration or open burning of ISW. |
|
none |
0 |
0.2 |
2.0 |
0 |
Nominal value is mean across all types of incineration technology and open burning (6500g/t waste) (Volume 5, Table 5.3), or 998.7 g/tonne. This is rounded up to 1 kg/tonne, or 0.001 kg/kg. |
||||
Input |
\(\text{CH}_4\) MSW Incineration Emission Factor |
Based on IPCC Tier 1 approach–\(\text{CH}_4\) emissions from incineration or open burning of MSW. |
|
none |
0 |
0.2 |
2.0 |
0 |
Nominal value is mean across all types of incineration technology and open burning (6500g/t waste) (Volume 5, Table 5.3), or 998.7 g/tonne. This is rounded up to 1 kg/tonne, or 0.001 kg/kg. |
||||
Input |
\(\text{CH}_4\) Recovery Factor Landfill Gas |
Factor representing how much methane is extracted from landfill gas that is recovered. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
\(\text{N}_2\text{O}\) Composting Emission Factor |
Emission factor representing emissions of nitrus oxide from composting of organic materials |
|
|
0 |
0.57 |
1.43 |
0 |
Default is set as mean between wet and dry weight factors from Volume 5, Table 4.1 in IPCC Guidelines for NGHG Inventories. |
||||
Input |
\(\text{N}_2\text{O}\) Incineration Emission Factor |
Based on IPCC Tier 2 approach (default emission factors with waste composition) |
|
all |
0 |
1.0 |
1.0 |
0 |
Default values taken from IPCC GNGHGI V5, C5, Tables 5.4 (MSW defaults, excluding plastic, wood, paper, and sludge) and 5.5 (industrial, sludge, wood, paper, and plastic). Note that the emission factors are unitless and are converted to tonne/tonne. |
||||
Input |
Average Annual Waste Transported Per Waste Collection Vehicle |
Average annual total waste collected per waste collection vehicle. Used to calculate a marginal increase in heavy transport transportation demand resulting from an increase in waste collection, which is passed to the transportation model. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Average Methane Correction Factor at Landfills |
The Methane Correction Factor represents different management approaches for solid waste disposal at landfills. See Volume 5, Chapter 3, Table 3.1 of IPCC Guidelines for National Greenhouse Gas Inventories for default MCFs. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Average Methane Correction Factor for Open Dumping |
The Methane Correction Factor represents different management approaches for solid waste disposal at landfills. See Volume 5, Chapter 3, Table 3.1 of IPCC Guidelines for National Greenhouse Gas Inventories for default MCFs. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Average Oxidization Factor at Landfills |
Oxidization factor (see V5, C3, Table 3.2) for landfills. The oxidization factor represents a practice at well-managed landfills of covering landfills with with \(\text{CH}_4\) oxidising material–e.g., soild or compost. Should not exceed 0.1. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Average VKMT Per Waste Collection Vehicle |
Average annual Vehicle Kilometers Traveled (VKMT) per waste collection vehicle. Used to calculate a marginal increase in heavy transport transportation demand resulting from an increase in waste collection, which is passed to the transportation model. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Biogas Recovery Factor |
Factor representing faction of biogas recovered for energy production. Recovery of biogass prevents emissions. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Elasticity of Municipal Solid Waste Produced to GDP per Capita |
The elasticity of waste per capita to GDP per capita, which is used to estimate increases in waste as population and GDP/capita rise. |
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Fraction of ISW Incineration Recovered for Energy |
Incineration can be open burning or for energy. This fraction \(a\) represents the how much ISW is incinerated for energy production. \(1 - a\) is then assumed to be some mix of open burning and icineration. Incinerable waste can be passed to the Energy model as a Fuel. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Fraction of Landfill Gas Recovered at Landfills |
Represents the proportion of methane emitted at landfills that is captured. This represents an average over the country across all landfills, as SISEPUEDE does not distinguish between sanitary landfills, controlled landfills, or other landfills. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Fraction of Landfill Gas Recovered for Energy |
Landfil gas can be captured and converted to energy. This fraction \(a\) represents the how much landfil gas that is captured is converted to energy. \(1 - a\) is then assumed to be recovered and not converted to energy (or flared). Landfill gas can be passed to the Energy model as a Fuel. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Fraction of MSW Incineration Recovered for Energy |
Incineration can be open burning or for energy. This fraction \(a\) represents the how much MSW is incinerated for energy production. \(1 - a\) is then assumed to be some mix of open burning and icineration. Incinerable waste can be passed to the Energy model as a Fuel. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Fraction of Methane Flared at Composting Facilities |
|
none |
0 |
1.0 |
1.0 |
0 |
||||||
Input |
Fraction of Non-Recycled Solid Waste Incinerated |
Proportion of non-recycled municipal waste that is burned in incineration facilities and in open burn sites. |
|
none |
0 |
1.0 |
1.0 |
1.0 |
0 |
||||
Input |
Fraction of Non-Recycled Solid Waste Landfilled |
Proportion of non-recycled municipal waste that is landfilled. Landfills include different levels of management |
|
none |
0 |
1.0 |
1.0 |
1.0 |
0 |
||||
Input |
Fraction of Non-Recycled Solid Waste Open Dumps |
Proportion of non-recycled municipal waste that is ends up in open dumpsites |
|
none |
0 |
1.0 |
1.0 |
1.0 |
0 |
||||
Input |
Fraction of Waste Composted |
Fraction of waste in category |
|
|
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Fraction of Waste Recycled |
Fraction of waste in category |
|
|
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Fraction of Waste Treated Anaerobically |
Fraction of waste in category |
|
|
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Historical Back Projection Growth Rate in Solid Waste Generation |
Primary a calibration parameter if using the back-projection method for solid waste. The growth rate at time \(t = 0\) is applied backwards to estimate waste landfilled in previous years. The back projection method should only be used in the absence of historical data. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Initial Composition Fraction Industrial Solid Waste |
Represents the fraction of all industrial solid waste represented by this type |
|
all |
0 |
1.0 |
1.0 |
2.0 |
0 |
Defaults taken as average between Central and South American from V5, C2 |
|||
Input |
Initial Composition Fraction Municipal Solid Waste |
Represents the initial fraction of all domestic solid waste represented by this type. Per capita growth rates in waste generated by category are projected by applying elasticities to changes in gdp/capita. |
|
all |
0 |
1.0 |
1.0 |
3.0 |
0 |
||||
Input |
Initial Per Capita Municipal Solid Waste Generated |
Represents the estimated quantity, in kg/person, of solid waste generated per person at time \(t = 0\). The total waste generated per person is then estimated for each waste composition category using the elasticity of waste production to income (GDP/Capita). |
|
none |
0 |
1.0 |
1.0 |
0 |
Country level data are available from the World Bank Waste Database. Additional regional defaults are available in V5, C2, Table 2.1 of IPCC GNGHGI for default rates by region. |
||||
Input |
K |
|
|
all |
0 |
1.0 |
1.0 |
0 |
Note that, for a half life t, the factor k is found as \(k = \ln(2)/t\). |
||||
Input |
Per GDP Industrial Solid Waste Generated |
Industrial waste generated per GDP |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Input |
Waste Per Capita Scale Factor |
|
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
\(\text{CH}_4\) Emissions from Anaerobic Biogas |
Emissions from anaerobic decomposition organic waste in biogas plants. This waste stream flow is used to generate energy. Note that methane leakage from these plants is assumed to be 5% with a range of 0 - 10 % (see 2006 IPCC GHG guidance Volume 5, Chapter 4, page 4.4) |
|
|
0 |
1.0 |
1.0 |
1 |
|||||
Output |
\(\text{CH}_4\) Emissions from Composting |
|
|
0 |
1.0 |
1.0 |
1 |
||||||
Output |
\(\text{CH}_4\) Emissions from Incineration |
Total \(\text{CH}_4\) emissions from incineration (combined MSW and ISW) |
|
none |
0 |
1.0 |
1.0 |
1 |
|||||
Output |
\(\text{CH}_4\) Emissions from Landfills |
Captures \(\text{CH}_4\) emissions from landfills (\(\text{CH}_4\) is assumed to be 50% of landfill gas. |
|
all |
0 |
1.0 |
1.0 |
1 |
|||||
Output |
\(\text{CH}_4\) Emissions from Open Dumping |
Captures \(\text{CH}_4\) emissions from open dumping. Aerobic decomposition can occur at lower levels with open dumping, but there is no collection of gas. |
|
all |
0 |
1.0 |
1.0 |
1 |
|||||
Output |
\(\text{CO}_2\) Emissions from Incineration |
Total \(\text{CO}_2\) emissions from incineration (combined MSW and ISW) |
|
none |
0 |
1.0 |
1.0 |
1 |
|||||
Output |
\(\text{N}_2\text{O}\) Emissions from Composting |
|
|
0 |
1.0 |
1.0 |
1 |
||||||
Output |
\(\text{N}_2\text{O}\) Emissions from Incineration |
Total \(\text{N}_2\text{O}\) emissions from incineration (combined MSW and ISW) |
|
none |
0 |
1.0 |
1.0 |
1 |
|||||
Output |
Biogas Recovered from Anaerobic Facilities |
Biogas is a mixture of methane, carbon dioxide, water vapor, hydrogen suflide, and other gases. See The EPA for an overview of anaerobic digestion and biogas. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Biogas Recovered from Landfills |
Mass of methane recovered from landfill gas that is colleted. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total ISW Recovered for Energy |
Total quantity of industrial solid waste that is recovered for energy use. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total MSW Recovered for Energy |
Total quantity of municipal solid waste that is recovered for energy use. |
|
none |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total Solid Waste Produced |
Total waste produced from industry and municipal sources. |
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total Waste Anaerobic Biogas |
Total quantity of waste sent to anaerobic biogas facilities. |
|
|
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total Waste Composted |
Total quantity of waste composted in tonnes. |
|
|
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total Waste Incinerated |
Total quantity of waste incinterated in tonnes. |
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total Waste Landfilled |
Total quantity of waste landfilled in tonnes. |
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total Waste Open Dumped |
Total quantity of waste open dumped in tonnes. |
|
all |
0 |
1.0 |
1.0 |
0 |
|||||
Output |
Total Waste Recycled |
Total quantity of waste recycled in tonnes. |
|
|
0 |
1.0 |
1.0 |
0 |