User’s Guide for Estimating Emissions and Sinks from Land Use Land-use Change and Forestry Using the State Inventory Tool January 2022


User's Guide for Estimating
Emissions and Sinks from Land
Use, Land-Use Change, and
Forestry Using the State
Inventory Tool

January 2022

Prepared by:
ICF

Prepared for:

State Energy and Environment Program,
U.S. Environmental Protection Agency

This section of the User's Guide provides instruction on using the Land Use, Land-Use
Change, and Forestry (LULUCF) module of the State Inventory Tool (SIT), and describes the
methodology used for estimating greenhouse gas (GHG) emissions and sinks from land use,
land-use change, and forestry at the state level.

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Table of Contents

1.1	Getting Started	2

1.2	Module Overview	4

1.2.1	Data Requirements	5

1.2.2	Tool Layout	5

1.3	Methodology	6

1.4	Uncertainty	24

1.5	References	24

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.1

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

1.1 Getting Started

The Land Use, Land-Use Change, and Forestry (hereafter, LULUCF) module was first
developed using Microsoft® Excel 2000. While the module will operate with older versions
of Excel, it functions best with Excel 2000 or later. If you are using Excel 2007 or later,
instructions for opening the module will vary as outlined in the Excel basics below. Some of
the Excel basics are outlined in the sections below. Before you use the LULUCF module,
make sure your computer meets the system requirements. In order to install and run the
LULUCF module, you must have:

• IBM-PC compatible computer with the Windows 95 operating system or later;

• Microsoft® Excel 1997 or later, with calculation set to automatic and macros
enabled;

• Hard drive with at least 20MB free; and

• Monitor display setting of 800 x 600 or greater.

Microsoft Excel Settings

Excel 2003 and Earlier: For the SIT modules to function properly, Excel must be set to
automatic calculation. To check this setting, launch Microsoft Excel before opening the
LULUCF module. Go to the Tools menu and select "Options..." Click on the "Calculations"
tab and make sure that the radio button next to "Automatic" is selected, and then click on
"OK" to close the window. The security settings (discussed next) can also be adjusted at
this time.

Excel 2007 and Later: For the SIT modules to function properly, Excel must be set to
automatic calculation. Go to the Formulas ribbon and select "Calculation Options." Make
sure that the box next to the "Automatic" option is checked from the pop-up menu.

Microsoft Excel Security

Excel 2003 and Earlier: Because the SIT employs macros, you must have Excel security
set to medium (recommended) or low (not recommended). To change this setting, launch
Microsoft Excel before opening the LULUCF module. Once in Excel, go to the Tools menu,
click on the Macro sub-menu, and then select "Security" (see Figure 1). The Security pop-
up box will appear. Click on the "Security Level" tab and select medium. When set to high,
macros are automatically disabled; when set to medium, Excel will give you the choice to
enable macros; when set to low, macros are always enabled.

When Excel security is set to medium, users are asked upon opening the module whether to
enable macros. Macros must be enabled in order for the LULUCF module to work. Once
they are enabled, the module will open to the control worksheet. A message box will
appear welcoming the user to the module. Clicking on the "x" in the upper-right-hand
corner of the message box will close it.

Excel 2007 and Later: If Excel's security settings are set at the default level a Security
Warning appears above the formula box in Excel when the LULUCF module is initially
opened. The Security Warning lets the user know that some active content from the
spreadsheet has been disabled, meaning that Excel has prevented the macros in the
spreadsheet from functioning. Because SIT needs macros in order to function properly, the
user must click the "Options" button in the security message and then select, "Enable this

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.2

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

content" in the pop-up box. Enabling the macro content for the SIT in this way only enables
macros temporarily in Excel but does not change the macro security settings. Once macros
are enabled, a message box will appear welcoming the user to module. Click on the "x" in
the upper right-hand corner to close the message box.

If the Security Warning does not appear when the module is first opened, it may be
necessary to change the security settings for macros. To change the setting, first exit out
of the LULUCF module and re-launch Microsoft Excel before opening the LULUCF module.
Next, click on the Microsoft Excel icon in the top left of the screen. Scroll to the bottom of
the menu and select the "Excel Options" button to the right of the main menu. When the
Excel Options box appears, select "Trust Center" in left hand menu of the box. Next, click
the gray "Trust Center Settings" button. When the Trust Center options box appears, click
"Macro Settings" in the left-hand menu and select "Disable all macros with notification."
Once the security level has been adjusted, open the Stationary Combustion module and
enable macros in the manner described in the preceding paragraph.

Viewing and Printing Data and Results

The LULUCF module contains some features to allow users to adjust the screen view and the
appearance of the worksheets when they are printed. Once a module has been opened, you
can adjust the zoom by going to the Module Options Menu, and either typing in a zoom
percentage or selecting one from the drop-down menu. In addition, data may not all
appear on a single screen within each worksheet; if not, you may need to scroll up or down
to view additional information.

You may also adjust the print margins of the worksheets to ensure that desired portions of
the LULUCF module are printed. To do so, go to the File menu, and then select "Print
Preview." Click on "Page Break Preview" and drag the blue lines to the desired positions
(see Figure 2). To print this view, go to the File menu, and click "Print." To return to the
normal view, go to the File menu, click "Print Preview," and then click "Normal View."

Figure 1. Changing Security Settings

D Microsoft Excel - Bookl

File Edit

View Insert

Format

Tools | Data Window Help I

| A1

Spelling... F7

A |

I B '

c I

Research... Alt+Click

H I

1 |

Error Checking...

Speech ~

Shared Workspace.,,

Share Workbook.,,

Track Changes ~

_8J

Compare and Merge Workbooks...

To]

Protection ~

TT]

Online Collaboration ~

Goal Seek,,,

J3]

Scenarios...

TjH

Formula Auditing ~

l6|

J71

| Macro ~ |

I Macros..,

Alt+F8

Tsl

Add-Ins...

Record Ne

w Macro...

J9J

AutoCorrect Options...

20J

Security,,,

Customize...

| Visual Basic Editor

Alt+Fll

Options,..

i Microsoft Script Editor

Alt+Shift+Fll

23^

—

Figure 2. Adjusting Print Margins

0 File Edit Module Options

Stale Inventory Tool ¦ Forest Management ar

Stote Inventory Tool - Emissions and Sinks From Forest Management and Land-Use Change

. Choose a State Colorado

This is very important - it selects the correct default variables foryoui
2. Verify the variables used for each sector analyzed in this tool.
Liming of Agricultural Soils

Emission Factors

Drag cursor
to resize page

Corbon 5eauestration Foctor

Savanna. 5 CHv'kg dry mc
Savanna, g N,0/kg dry matter cJ
Forests, c CHvkg in mat-er ca

Default Value Value

;tr>

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.3

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Module 8 - Land Use, Land-Use Change, and Forestry Module

September 2019

1.2 Module Overview

This User's Guide accompanies and explains the LULUCF module of the SIT. The SIT was
developed in conjunction with EPA's Emissions Inventory Improvement Program (EIIP).

Prior to the development of the SIT, EPA developed the States Workbook for estimating
greenhouse gas emissions. In 1998, EPA revisited the States Workbook and expanded it to
follow the format of EIIP guidance documents for criteria air pollutants. The result was a
comprehensive, stepwise approach to estimating greenhouse gas emissions at the state
level. This detailed methodology was appreciated by states with the capacity to devote
considerable time and resources to the development of emission inventories. For other
states, the EIIP guidance was overwhelming and impractical for them to follow from scratch.
EPA recognized the resource constraints facing the states and developed the SIT. The ten
modules of the SIT corresponded to the EIIP chapters and attempted to automate the steps
states would need to take in developing their own emission estimates in a manner that was
consistent with prevailing national and state guidelines.

Because most state inventories developed today rely heavily on the tools, User's Guides
have been developed for each of the SIT modules. These User's Guides contain the most
up-to-date methodologies that are, for the most part, consistent with the Inventory of U.S.
Greenhouse Gas Emissions and Sinks. Volume VIII of the EIIP guidance is a historical
document that was last updated in August 2004, and while these documents can be a
valuable reference, they contain outdated emissions factors and, in some cases, outdated
methodologies. States can refer to Volume VIII of the EIIP guidance documents if they are
interested in obtaining additional information not found in the SIT or the companion User's
Guide.

When humans use and alter the biosphere through land-use change and forest management
activities, the balance between the emission and uptake of greenhouse gases (GHGs)
changes, affecting their atmospheric concentration; this balance between emission and
uptake is known as net GHG flux. Such activities can include clearing an area of forest to
create cropland, restocking a logged forest, draining a wetland, or allowing a pasture to
revert to grassland. Carbon in the form of yard trimmings and food scraps can also be
sequestered in landfills, as well as in trees in urban areas. In addition to carbon flux from
forest management, urban trees, landfills, and agricultural soils (i.e., cropland and
grassland), other sources of GHGs under the category of land use, land-use change, and
forestry are emissions of methane (Cl-U) and nitrous oxide (N2O) from forest fires, and N2O
emissions from fertilization of settlement soils.

The LULUCF module calculates CO2, CH4, and N2O emissions from fertilization of settlement
soils, and forest fires, as well as carbon flux from forest management, urban trees,
landfilled yard trimmings and food scraps, and agricultural soils. The LULUCF module no
longer estimates CO2 emissions from Liming of Soils and Urea Fertilization. These categories
are now estimated in the Agriculture module for consistency with the Inventory of U.S.
Greenhouse Gas Emissions and Sinks.

The module provides default data for most inputs; however, if you have access to a more
comprehensive or state-specific data source, it should be used in place of the default data.
If using outside data sources, or for a more thorough understanding of the tool, please refer
to the following discussion for data requirements and methodology.

State Greenhouse Gas Inventory Tool User's Guide

1.4

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

1.2.1 Data Requirements

To calculate GHG emissions from land use, land-use change, and forestry, the data listed in
Table 1 are required inputs (again, note that defaults are available for most of these data).

Table 1. Required data inputs for the LULUCF module.

Forestry
Worksheets

Input Data Required

Forest Carbon Flux
(Forest Land Remaining
Forest Land, Land
Converted to Forest
Land, and Forest Land
Converted to Land)

Carbon emitted from or sequestered in aboveground biomass,
belowground biomass, dead wood, litter, mineral and organic soils,
drained organic soils, wood products and landfills (million metric tons)

Urban Trees

Carbon sequestration factor for urban trees (metric ton C/hectare/year)
Total urban area (square kilometers)

Urban area tree cover (percent)

N2O from Settlement
Soils

Direct N2O emission factor for managed soils (percent)

Total synthetic fertilizer applied to settlements (metric tons nitrogen)

Non-C02 Emissions from
Forest Fires

Emission factors for CH4 and N2O emitted from burning forest and
savanna (grams of gas/kilogram of dry matter combusted)
Combustion efficiency of different vegetation types (percent)
Average biomass density (kilograms dry matter per hectare)

Area burned (hectares)

Landfilled Yard
Trimmings and Food
Scraps

Grass, leaves, and branches constituting yard trimmings (percent)

Yard trimmings and foods scraps landfilled, 1960-present (tons)

Initial carbon content of yard trimmings and food scraps (percent)
Dry weight/wet weight ratio of yard trimmings and foods scraps (percent)
Proportion of carbon stored permanently for yard trimmings and foods
scraps (percent)

Half-life of deqradable carbon for yard trimmings and foods scraps (years)

Agricultural Soil Carbon
Flux

Carbon emitted from or sequestered in mineral and organic soils on
cropland and grassland (million metric tons)

1.2.2 Tool Layout

Because there are multiple steps to complete within the LULUCF module, it is important to
understand of the module's overall design. The layout of the LULUCF module and the
purpose of its worksheets are presented in Figure 3.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.5

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Figure 3: Flow of Information in the LULUCF Module*

Control Worksheet

Individual Sector Worksheets

1. Choose a State

2. Enter Forest Carbon Flux Data ¦*

~ 2. Forest Carbon Flux

Enter data on annual change in carbon stocks of various forest pools.

2a. Forest Land Remaining Forest Land

Default data pulled from FRF Carbon Flux worksheet.

2b. Land Converted to Forest Land

Default data pulled from LCF Carbon Flux worksheet.

2c. Land Converted to Forest Land

Default data pulled from FCL Carbon Flux worksheet.

3.-6.

3. Urban Trees

Verify Variables for Each Sector on Control Sheet

I Enter data on total urban area and percent of urban area with tree cover.

Complete Sector Worksheets

4. N20 from Settlement Soils

)

Enter data on fertilizer applied to settlement soils.

5a. CH4 Emissions from Forest Fires

Enter data on area of forest and savanna burned, by forest type.

5b. N20 Emissions from Forest Fires

Data pulled from CH4 Emissions from Forest Fires worksheet.

6. Landfilled Yard Trimmings and Food Scraps

Enter data on yard trimmings and food scraps.

7. Enter Agricultural Soil Carbon Flux Data

~ 7. Agricultural Soil Carbon Flux

8. View Summary Data *

Enter data on annual change in carbon stocks in agricultural soils.

9. Export Data ~—-—

—~ Summary Data

Presented in both table and graphical formats in MMTC02E.

—*¦ Uncertainty

Review information on uncertainty associated with default data.

* These worksheets are the primary worksheets used in the LULUCF module; subsequent worksheets
are used to populate the default data and are provided for informational purposes only.

1.3 Methodology

This section provides a guide to using the LULUCF module of the SIT to estimate GHG
emissions and sequestration from land use, land-use change, and forestry. Within the
LULUCF module, there are six sections: forest carbon flux; urban trees; N2O from
settlement soils; non-CC>2 emissions from forest fires; carbon storage in landfilled yard
trimmings and food scraps; and agricultural soil carbon flux. Because the methodology
varies considerably among these sources/sinks, the details of each will be discussed in its
respective step, following this general methodology discussion.

The LULUCF module will automatically calculate emissions after you enter the factors on the
control worksheet and the required activity data on the individual sector worksheets. The
tool provides default sector data for most sectors. The exception is forest fires where you
will have to use an outside data source for area of forest burned per year (see Box 1 for
suggested data sources).

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.6

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Box 1: Forest Fire Data Sources

• Data are available from the National Interagency Coordination Center, which compiles fire
records from Situation and Incident Status Summary (ICS-209) Reports. These records
provide the number of acres burned by forest fire by state, and can be found in Table 12.4-2 of
the EIIP Guidance or online at https://www.nifc.gov/fireInfo/fireInfo statistics.html

• To obtain the most accurate emission estimates, it is necessary to have information on the
type of forests that have burned, as different types of forests contain differing amounts of
combustible biomass. To further refine the analysis, information on specific burns and forest
types can be found in the U.S. Federal Wildland Fire Management's website:

http: //www. fs. fed. us/fi re/.

• To obtain accurate emissions for both wildfires and prescribed burning, users may directly
consult FOFEM, which is available for download at https://www.firelab.org/proiect/fofem.
Additional instructions for using the model are provided on the website.

• Land management agencies (e.g., the U.S. Forest Service, Bureau of Land Management, State
Natural Resource Divisions) in each state maintain statistics on the areas and types of forests
within their jurisdiction that have burned.

• State-level estimates of non-C02 emissions from forest fires are available for certain states
from the U.S. Forest Service's publication, "Greenhouse gas emissions and removals from
forest land, woodlands, and urban trees in the United States. 1990-2019" (see Appendix 1 of
the publication).

There are nine general steps involved in estimating emissions using the LULUCF module: (1)
select a state; (2) select an option for forest carbon flux; (3) enter emission factors and
activity data for urban trees; (4) enter emission factors and activity data for N2O from
settlement soils; (5) enter emission factors and activity data for non-CC>2 emissions from
forest fires; (6) enter emission factors and activity data for landfilled yard trimmings and
food scraps; (7) select an option for agricultural soil carbon flux; (8) review summary
information; and (9) export data. The general equations used to calculate GHG emissions
from land use, land-use change, and forestry are provided below.

Step (1) Select a State

To begin, select the state you are interested in evaluating. By selecting a state, the rest of
the tool will automatically reset to reflect the appropriate state default data and
assumptions for use in subsequent steps of the tool.

Step (2) Select an Option for Forest Carbon Flux

Control Worksheet

The control worksheet allows you to either select the default data provided or to enter user-
specified data to be used throughout the tool. To proceed with the default data, select the
first radio button under step 2 on the control worksheet. Default data are available for three
land-use categories: Forest Land Remaining Forest Land, Land Converted to Forest Land,
and Forest Land Converted to Land. These three categories are summed together on the
Summary tab to calculate Net Forest Carbon Flux. If you would like to use your own state-
specific data, select the second radio button under step 2 of the control worksheet. See
Figure 4 for an example of the radio buttons in step 2.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.7

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Module 8 - Land Use, Land-Use Change, and Forestry Module January 2022

Figure 4. Control Worksheet for the LULUCF Module

2 State Inventory Tool - Emissions and Sinks From Land Use, Land-Use Change, and Forestry

3 1

51 %

6 J1. Choose a State California ~

7 This is very important - it selects the correct default variables for your state.

Choose a State

Consult User's Guide

Reset All!

Select All Defaults

Check/Uncheck All

10 2. Forest Carbon Flux (Forest Land Remaining Forest Land, Land Converted to Forest Land, and Forest Land Converted to Land)

P Click here if you do not hoive any date on forest carton flux and would like "to use defau It estimates by ihe USD A Forest Service
{no default date are ava i lable f o r AK, HI, or DC).

3. C Storage in Urban Trees

Carbon Sequestration Factor

metric ton C/hectare/year in California

4. NgO from Settlement Soils

Emission Factor

Direct NJzO Emission Factor for Managed Soils

Default Value

2.8

Forest Carbon Flux
Radio Buttons

12 (* flick here if you would like to uce your own data art forest carbon flux*

T3]

15 3.- 6. Enter emission factors and proceed to the corresponding worksheet to enter activity data for the following:

18
1U

2 b
2fj

27J

28]

30
3TJ
32
¦SS]

34
35]

3b
3/

38]

39
4U

5. f*4on-CO? From Forest Fires
Emission Factors

Savanna, g CH
>

As a result of biological processes (e.g., growth and mortality) and anthropogenic activities
(e.g., harvesting, thinning, and other removals), carbon is continuously cycled through
ecosystem components, as well as between the forest ecosystem and the atmosphere. For
example, the growth of trees results in the uptake of carbon from the atmosphere and
storage in living trees. As these trees age, they continue to accumulate carbon until they
reach maturity, at which point their carbon storage remains relatively constant. As trees die
or drop branches and leaves on the forest floor, decay processes will release carbon to the
atmosphere and also increase soil carbon. Some carbon from forests is also stored in wood
products, such as lumber and furniture; and also in landfills, because when wood products
are disposed of, they do not decay completely, and a portion of the carbon gets stored
indefinitely, as with landfilled yard trimmings and food scraps. The net change in forest
carbon is the change in the amount of carbon stored in each of these pools (i.e., in each
ecosystem component) over time. This section presents the methodology for calculating
forest carbon flux.

After completing the control worksheet for this sector, use the gray arrows to navigate to
the Forest Land Remaining Forest Land worksheet.

Forest Land Remaining Forest Land Worksheet

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.8

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

If you are using the default data for forest carbon flux estimates, there is no further
information to enter. Figure 5 shows the default worksheet for Forest Land Remaining
Forest Land.

Figure 5. Example of Forest Land Remaining Forest Land Worksheet Using Default

Data

A B	C , D, E 	F	G i H i I i

2a. Forest Land Remaining Forest Land in California

Two methodologies are used 1o calculate carbon emissions/storage (flux) from forest carbon using USDA Forest Service estimates of each state's forest carbon stocks

(1)	The first methodology applies to aboveground biomass belowground biomass dead wood, forest floor litter, and soil carbon from mineral and organic soils USDA Forest Service
lates for each state's forest carbon stocks are provided for 1990-2018. These estimates are based on a publication titled "Greenhouse gas emissions and removals from forest land,

woodlands, and urtian trees in the United States, 1990-2018. " Note: Met C03 flux estimates presented in the table below are from the Forest Land Remaining Fores! Land category The
following tabs provide estimates for Land Converted to Forest Land and Forest Land Converted to Land. These land-use change categories are combined on the Summary tab to provide an
estimate of total forest carbon flux No defaults are available for Alaska. Hawaii, or the District of Columbia. Totals may not sum to national or state-level totals due to independent rounding

(2)	The second methodology used applies to wood products and landfills (i.e. harvested wood products). Since the latest USDA Forest Sen
lates for harvested wood products, default carbon emissions/storage are calculated by using USDA Forest Service estimates of each st

1997 Changes from 1987-1992 and from 1992-1997 are each divided by 5 (the number of intervening years) to determine the average ann
applied for each year, giving total annual change. For the years 1998-2018, the average annual change for 1992-1997 is used as proxy data

Users may also enter their own data This may be done by selecting the appropriate option in Step 2 on the Control worksheet For more inrei
Use Change, and Forestry chapter of the User's Guide.

Continue to Land
Converted to Forest

Return to Control

On default sheet, data are
already provided

Default data for Aboveground and Belowground Biomass, Dead Wood, Litter, and Soil Carffon

Net Sequestration/Emissions from Forest Land Remaining Forest Land

7

8



1990

1991

1992

1993

1994

1995

1996

mmtco2e |

1997 1998

r 1999

2000

2001

2002

2003

2004

2005

9

Aboveground Biomass

(28.59)

(28.35)

(28.11)

(27.87)

(27.64)

(27.42)

(27.19)

(26.97)

(26.74)

(26.52)

(26.29)

(26.07)

(25.84)

(25.62)

(25.38)

(25.14)

10

Belowground Biomass

(6.28)

(6.23)

(6.18)

(6.12)

(6.08)

(6.03)

(5.98)

(5.93)

(5.88)

(5.83)

(5.78)

(5.73)

(5.69)

(5.64)

(5.58)

(5.53)

11

Oeadwood

(5.68)

(5.72)

(5.76)

(5.79)

(5.82)

(5.84)

(5.87)

(5.89)

(5.91)

(5.94)

(5.96)

(5.99)

(6.01)

(6.04)

(6.04)

(6.04)

12

Litter

(0.38)

(0-37)

(0-37)

(0.36)

(0.36)

(0.36)

(0.36)

(0.35)

(0.35)

(0.35)

(0.35)

(0.34)

(0.34)

(0.34)

(0.33)

(0.32)

13

Soil (Mineral)

0.61

0.60

0.58

0.57

0.57

0.57

0.57

0.58

0.58

0.58

0.58

0.58

0.58

0.59

0.58

0.58

14

Soil (Organic)

(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)







1b

brained Organic Soil

































16

Total

(40.32)

(40.07)

(39.82)

(39.58)

(39.32)

(39.07)

(38.82)

(38.56)

(38.31)

(38.06)

(37.80)

(37.55)

(37.30)

(37.04)

(36.75)

(36.45)

Next, click the gray navigational arrow to continue to the Land Converted to Forest Land
worksheet.

Land Converted to Forest Land Worksheet

This tab calculates net sequestration/emissions from Land Converted to Forest Land. This
category includes Cropland Converted to Forest Land, Grassland Converted to Forest Land,
Settlements Converted to Forest Land, and Other Land Converted to Forest Land. There is
no further information to enter on this tab if you are using the default data for forest carbon
flux. Figure 6 shows the default worksheet for Land Converted to Forest Land.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.9

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Figure 6: Example of Land Converted to Forest Land Worksheet Using Default Data

2b. Land Converted to Forest Land in California

This methodology applies lo aboveground biomass, belowground biomass dead wood, forest floor litter, and s«l carbon from mineral soils within the Land Converted to Forest
Land category This category includes net sequestration/emissions from Cropland Converted to Forest Land. Grassland Converted to Forest Land Settlements Converted to
Forest Land: and Other Land Converted to Forest Land These estimates are based on a publication titled "Greenhouse gas emissions and removals from forest land,
woodlands, and urban trees in the United States. 1990-2018" Total values for forest carbon flux are located on the Summary tab. Note: No defaults are available for Alaska,
Hawaii, or the District of Columbia Totals may not sum to national or state-level totals due to independent rounding.

Continue to Forest Land
Converted to Land

5 Default data for Aboveground and Belowground Biomass, Dead Wood, Litter, and Soil Carbon

On default sheet, data are
already provided

Net Sequestration/Emissions from Land Converted wForest Land



1990

1991

1992

1993

1994

199S

1996

MMTCOjE
1997 1998

1999 I

£*2000

2001

2002

2003

2004

Aboveground Biomass

(2.09)

(2.09)

(2.08)

(2.08)

(2.07)

(2.07)

(2.06)

(2.06)

(2-05)

(2.04) ™

(2.04)

(2.03)

(2.03)

(2.02)

(2.02)

Belowground Biomass

(0.41)

(0.40)

(0.40)

(0.40)

(0.40)

(0.40)

(0.40)

(0.40)

(0.40)

(0.40)

(0.40)

(0.39)

(0.39)

(0.39)

(0.39)

Deadwood

(0.52)

(0.52)

(0.52)

(0.52)

(0.52)

(0.51)

(0.51)

(0-51)

(0.51)

(0-51)

(0-51)

(0.51)

(0.51)

(0.50)

(0.50)

Litter

(0.93)

(0.93)

(0.93)

(0.92)

(0.92)

(0.92)

(0.92)

(0.91)

(0.91)

(0.91)

(0.91)

(0.90)

(0.90)

(0.90)

(0.90)

Soil (Mineral)

(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)

(o.oi)

(0.01)

Total

(3.95)

(3.94)

(3.93)

(3.92)

(3.91)

(3.90)

(3.89)

(3.88)

(3.87)

(3.86)

(3.85)

(3.85)

(3.84)

(3.83)

(3.82)

16 Subtotals by Land-Use Change Category

Net Sequestration/Emissions from Cropland Converted to Forest Land

Next, click the gray navigational arrow to continue to the Forest Land Converted to Land
Worksheet.

Forest Land Converted to Land Worksheet

This tab calculates net sequestration/emissions from Forest Land Converted to Land. This
category includes Forest Land Converted to Cropland and Forest Land Converted to
Settlements. There is no further information to enter on this tab if you are using the default
data for forest carbon flux. Figure 7 shows the default worksheet for Forest Land Converted
to Land.

Figure 7: Example of Forest Land Converted to Land Worksheet Using Default Data

A	B	CPE	F	G	H

2c. Forest Land Converted to Land in California

This methodology applies to aboveground biomass, belowground biomass dead wood, forest floor litter, and soil carbon from mineral soils within the Forest Land Converted to
Land category This category includes net sequestration/emissions from Forest Land Converted to Cropland and Forest Land Converted to Settlements. These estimates are
si on a publication titled "Greenhouse gas emissions and removals from forest land, woodlands and urban trees in the United States, 1990-2018." Total values for forest
carbon flux are located on the Summary tab. Note: No defaults are available for Alaska, Hawaii, or the District of Columbia Totals may not sum to national or state-level totals
due to independent rounding.

Users may also enter their own data This may be done by selecting the appropriate option in Step 2 on the Control worksheet. For more inform;

Use, Land-Use Change and Forestry chapter of the User's Guide.

Return to
, Control Sheet

Default data for Aboveground and Belowground Biomass, Dead Wood, Litter, and Soil Carbor-

Net Sequestration/Emissions from Forest Land <



1990

1991

1992

1993

1994

1995

1996

MMTCOjE
1997

1998

Aboveground Biomass

L12

1.13

L14

1.15

1.15

1.16

1.18

1.19

L20

Belowground Biomass

0.22

0.22

0.22

0.22

0.22

0.22

0.23

0.23

0.23

Deadwood

0.17

0.17

0.17

0.17

0.17

0.18

0.18

0.18

0.18

Litter

0.36

0.36

0.37

0.37

0.37

0.38

0.38

0.39

0.39

Soil (Mineral)

0.02

0.02

0.02

0.03

0.03

0.03

0.03

0.03

0.03

Total

1.89

1.90

1.92

1.94

1.95

1.97

1 99

2.01

2.03

On default sheet, data are
already provided

rerted to Land

£000 2001 2002 2003

1.21
0.23
0.19
0.40
0.03
2.OS

1.22
0.24
0.19
0.40
0.03
2.08

L23
0.24
0.19
0.40
0.03
2.10

1.24
0.24
0.19
0.41
0.03
2.11

16 Subtotals by Land-Use Change Category

1.25
0.24
0.20
0.41
0.03
2.13

L26
0.24
0.20
0.42
0.03
2.IS

Net Sequestration/Emissions from Forest Land Converted to Cropland

If you are using your own data on forest carbon flux, enter carbon flux data for
aboveground biomass, belowground biomass, dead wood, litter, mineral and organic soils,
drained organic soil, and wood products and landfills in the green cells on the C Flux-User

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.10

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Data tab. Figure 8 shows the worksheet where you will enter this forest carbon flux data.
The method used for calculating forest carbon flux is shown in Equation 1. The calculation
is a sum of the fluxes for above- and belowground biomass, dead wood, litter, mineral and
organic soils, drained organic soil, and wood products in use and in landfills. Once this
sector worksheet is complete, use the gray navigational arrow to return to the control
worksheet and proceed to the next step.

Equation 1. Forest Carbon Flux Equation

Emissions or Sequestration (MMTCO2E) =

Sum of carbon fluxes from aboveground biomass, belowground biomass, dead wood,
litter, mineral and organic soils, drained organic soil, and wood products and landfills

Step (3) Enter Emission Factors and Activity Data for Urban Trees
Control Worksheet

On the control worksheet, enter a carbon sequestration factor for urban trees in the
appropriate yellow cell (metric tons of carbon per hectare per year). Default state-specific
estimates of net sequestration are provided from Nowak et al. (2013). If the user-specific
inputs do not match the default data in the control worksheet (i.e., the default value is
overwritten), the text will appear red.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.11

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Trees in urban areas represent approximately 5.5 percent of total United States tree canopy
cover (Nowak and Greenfield 2012). Furthermore, because trees in urban areas grow in
relatively open surroundings, their growth and carbon sequestration are disproportionately
large relative to forests. This section presents the methodology for calculating carbon
sequestered by urban trees in your state.

After entering the appropriate sequestration factor, use the gray arrows to navigate to the
Urban Trees worksheet.

Urban Trees Worksheet

Within the Urban Trees worksheet, enter data on the total urban area in your state (in
square kilometers), as well as the average percent of urban area covered by trees, in the
yellow cells. An example of this worksheet is shown in Figure 9. Equation 2 shows the
method used to calculate carbon sequestration in urban trees.

Default urban areas are taken from Nowak et al. (2005) and the U.S. Census (1990, 2002,
and 2012). Default state-specific percentages of urban tree cover are taken from Nowak
and Greenfield (2012). Once this worksheet is complete, use the gray navigational arrow to
return to the control worksheet and proceed to the next step.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.12

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Equation 2. Urban Trees Equation

Sequestration (MMTCO2E) =

Total Urban Area (km2) x Urban Area with Tree Cover (%)
x 100 (ha/km2) x C Sequestration Factor (metric tons C/ha/yr) x 44/12 (ratio of CO2 to

C) -r 1,000,000 (to yield MMTCO2E)

Figure 9. Example of Carbon Sequestration Factor Applied in the Urban Trees

Worksheet

A B , C D

3. Urban Trees in California

Changes in carbon stocks in urban trees are equivalent to tree growth minus biomass losses resulting from pruning and mortality. Net carbon sequestration can
be calculated using data on crown cover area or number of trees. Default state-specific data are given, or states may apply other state-specific values where
available through sampling, aerial photography, or from municipal agencies that maintain urban vegetation data.

To estimate C02 sequestration by urban trees, the following steps are required: (1) obtain data on the area of urban tree cover; (2) calculate C02 flux; and (3)
convert units to metric tons of carbon dioxide equivalent (MTC02E). This tool uses default urban area data multiplied by a state-specific estimate of the percent
of urban area with tree cover to estimate the total area of urban tree cover. This default data, from Nowak et al. 2005, Nowak and Greenfield 2012, and the U.S.
Census, represents urban area tree coverage for years 1990, 2000, and 2010. Estimates of urban area in the intervening years (1990-1999; 2001-2009) and
subsequent years (2011-2016) are interpolated and extrapolated, respectively. State-specific net carbon sequestration rates are taken from Nowak et al. 2013
and multiplied by urban area to calculate CO, flux. States are encouraged to use state-specific data when available.

For more informatic

Required Data on Urban
Area and Tree Cover

Forestry chapter of the User's Guide.

Return to Control
Sheet

Year

Total Urban Arty

(km2) //

1990

jy17.600.00

1991

^ 17,898.40

1992

18,196.80

1993

18.495.20

1994

18,793.60

1995

19,092.00

1996

19,390.40

1997

19,688.80

1998

19,987.20

1999

20,285.60

Percent of Urban Area
with Tree Cover

25%
25%

100|
100|

Carbon
Sequestration Factor
(metric ton C/heetare/year)

^^b2.88|

Carbon Sequestration
(MMTCOzE)

Carbon

Sequestration Factor
(from Control)

5.14
5.22

Step (4)

Soils

Enter Emission Factors and Activity Data for N2O from Settlement

Control Worksheet

Of the fertilizers applied to soils in the United States, approximately 10 percent are applied
to lawns, golf courses, and other landscaping occurring within settled areas. This section of
the LULUCF module estimates N2O emissions due to the application of fertilizers to
settlement soils. On the control sheet you must enter an emission factor that will be used
to calculate direct emissions due to fertilizer applications. The default value of 1 percent
comes from IPCC (2006). If the user-specific inputs do not match the default data in the
control worksheet (i.e., the default value is overwritten), the text will appear red.

After entering the appropriate emission factor, use the gray arrows to navigate to the Non-
CO2 from Settlement soils worksheet.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.13

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

N2O from Settlement Soils Worksheet

To complete this worksheet enter the amount of synthetic fertilizer applied (in metric tons of
nitrogen) in the light blue cells (Figure 10). Emissions are calculated by multiplying the
fertilizer data by the emission factor for direct emissions of N2O (1.0 percent) to obtain the
amount of emissions in INhO-N/yr. This number is then converted from MT N2O-N to MT N2O
by multiplying by the ratio of N2O/N2O-N (44/28). This is then converted to MMTCO2E by
dividing by 1,000,000 and multiplying by the GWP of N2O. This calculation is shown in
Equation 3. Once this worksheet is complete, use the gray navigational arrow to return to
the control worksheet and proceed to emissions from forest fires.

Figure 10. Example of Fertilizer Data Applied in the Settlement Soils Worksheet

A

4.

B _C	 D	E FGH	I	J	K	L	MNO

N20 from Settlement Soils in California	

Settlement soils include all developed land, including transportation infrastructure and human settlements of any size, unless they are already
included under other categories.

N20 emissions from settlement soils are calculated by multiplying the total synthetic fertilizer applied to settlements by the emission factor and the
factor used to convert nitrogen to N20 emissions (44/28). The calculated direct N20 emissions are then multiplied by the global warming potential of
N20 and converted to million metric tons carbon dioxide equivalent.

For more information, please consult the User's Guide on estimating emissions from Land Use, Land-Use Change, and Forestry activities.

Return to
Control Sheet

Required data on
applied fertilizer

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

Clear AW Data

298
298

Carbon
Dioxide
Emissions
(MTCO2E)

230,114

215,624

214,642

257,513

279,360
237,871
223,366
248,430

273,647

Total
Carbon
Dioxide
Emissions
(MMTCO2E)

0.230

0.216

0.215

0.258

0.279
0.238
0.223
0.248

0.274

Equation 3. Equation for Direct N2O Emissions from Settlement Soils

Emissions (MMTCO2E) =

Total Synthetic Fertilizer Applied to Settlement Soils (metric ton N) x
Emission Factor (percent) x 0.01 (metric tons N20-N/metric ton N) x
44/28 (Ratio of N20 to N2O-N) X 298 (GWP) -r 1,000,000
(MT/MMTCO2E)

Step (5) Enter Emission Factors and Activity Data for Non-C02 from Forest
Fires

Control Worksheet

On the control worksheet, the following data must be entered in the appropriate yellow cells
for forest fires: (1) emission factors for N2O and ChU for forest and savanna (grams of gas
per kg dry matter combusted), (2) combustion efficiency by vegetation type (%), and (3)

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.14

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

average biomass density in the state (kg dry matter per hectare). Default emission factors
and combustion efficiencies are from IPCC (2006). Default biomass densities are adapted
from Smith et al. (2001) and U.S. EPA (2003). States are encouraged to use this more
detailed data if it is available and well documented. If the user-specific inputs do not match
the default data in the control worksheet (i.e., the default value is overwritten), the text will
appear red.

When a forest (or savanna) burns, the CO2 emissions are included in the overall flux of
forest carbon that is calculated in the forest carbon flux worksheet. However, forest fires
also cause emissions of N2O and ChU that are not accounted for under forest carbon flux
because they are non-CC>2 emissions. This section presents the methodology for calculating
N2O and CH4 emissions from forest fires.

After entering the appropriate emission factors for forest fires, use the gray arrows to
navigate to the Non-CC>2 from Forest Fires worksheet.

Non-C02 from Forest Fires Worksheets

Within the Forest Fires worksheet, enter the area (hectares) burned per year in the pink
cells. Because there is no default data available on area burned by state, you must rely on
outside sources for this information (see Box 1 for suggestions). Equation 4 shows the
method used to calculate N2O and ChU emissions from forest fires. An example of this
worksheet is shown in Figure 11. Once this sector worksheet is complete, use the gray
navigational arrow to return to the control worksheet and proceed to the next category.

Equation 4. Forest Fires Emissions Equation

Emissions (MMTCO2E) =

Area Burned (ha) x Average Biomass Density (kg dry matter/ha) x Combustion
Efficiency (%) x Emission Factor (g gas/kg dry matter burned) x GWP

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.15

-------
Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Figure 11. Example of Forest Fire Data Applied in the Forest Fire Worksheet

A B | C D E F

5a. Methane Emissions from Forest Fires in California

Biomass burned in forest fires emits C02, CH^ and N20, in addition to many other gases and pollutants. C02 emissions are
inherently captured under total carbon flux calculations, but CH4 and N20 must be estimated separately. All fires—wildfires and
prescribed burns—emit these greenhouse gases.

Calculating the emissions of CH^ and N20 from burned forests requires determining the amount of carbon released by the fire
(by multiplying the area burned, the fuel load, and the combustion efficiency) and then factoring in the emission ratio for each
gas. No default data are available for area burned by forest type, but defaults are available for the other data points. States
may choose to use state-specific data when available. The emission factors used in this tool are averages; to obtain more

7 Forest Fires

Required data
on area burned
by forest fires

"l)fem>. Addition

Use, Land-Us

Forest Type

Primary tropical forests
Secondary tropical forests
Tertiary tropical forests
Boreal forest
Eucalypt forests
Other temperate forests
Shrublands

Savanna woodlands (early dry season burns)
Savanna woodlands (mid/late season burns)
Total

20 Forest Fires

s may directly consult FOFEM. whicl

Combustion
Efficiencies
(from Control)

Return to Control Sheet

So to Burning N2O Sheet

Average Biomass Density

Emission Factor (g/kg

Emission Factors
(from Control)

Forest Type

Primary tropical forests
Secondary tropical forests

Biomass Density
(from Control)

Average Biomass Density

(kg d m. ! ha)

150,061

Combustion
efficiency

Emission Factor (g/kg
dry matter burned)

MTOH4 Emitted

(kg d.m. / ha)

\ efficiency

dry matter burned)

MTCHa bWiTTM CHTSW11

bw. 3 i>m 'mmtco2e

150,061

x»

36% ,

8J J

- x 25

150,061

55% x

x 25

150,061

59% x

8.1 fft

x 25

150,061

34% x

8.1

x 25

150,061

63% x

8.1

x 25

150,061

45% x

8.1

x 25

150,061

72% x

8.1

x 25

150,061

40% x

4.6

x 25

150,061

74% x

4.6

x 25

Emissions MMTCOzE

36% x

8.1

X 25

55% x

8.1

x 25

Step (6) Enter Emission Factors and Activity Data for Landfilled Yard
Trimmings and Food Scraps

Control Worksheet

When wastes of biogenic origin (such as yard trimming and food scraps) are landfilled and
do not completely decompose, the carbon that remains is effectively removed from the
global carbon cycle. This section of the LULUCF module estimates the carbon stored in
landfills by yard trimmings and food scraps.

Because the Landfilled Yard Trimmings and Food Scraps sector involves complicated
calculations, the gray navigational arrow on the control worksheet takes you directly to the
Landfilled Yard Trimmings and Food Scraps worksheet.

Landfilled Yard Trimmings and Food Scraps Worksheet

The Landfilled Yard Trimmings and Food Scraps sector worksheet calculates net carbon flux
by estimating the change in landfilled carbon stocks between years, based on
methodologies presented in IPCC (2003) and IPCC (2006). The LULUCF module uses
Equation 5 to calculate carbon sequestration associated with landfilled yard trimmings and
food scraps. Carbon stock estimates were calculated by: determining the mass of landfilled
carbon resulting from yard trimmings or food scraps discarded in a given year; adding the
accumulated landfilled carbon from previous years; and subtracting the portion of carbon
landfilled in previous years that has decomposed.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.16

-------
Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Equation 5. Landfilled Yard Trimmings and Food Scraps Equation

LFC j,t = I Wj,

„ x (1 - MQ) x ICCi x {[CSi x ICQ] + [(1 - (CSi x ICQ )) x e kx(t n) ]>

n

where,



t

= the year for which carbon stocks are being estimated,

LFC i,t

= the stock of carbon in landfills in year t, for waste i (grass, leaves,



branches, food scraps)

Wi,n

= the mass of waste i disposed in landfills in year n, in units of wet



weight

n

= the year in which the waste was disposed, where 1960 < n < t

MCi

= moisture content of waste i,

CSi

= the proportion of initial carbon that is stored for waste i,

ICCi

= the initial carbon content of waste i,

e

= the natural logarithm, and

k

= the first order rate constant for waste i, and is equal to 0.693 divided



by the half-life for decomposition.

To determine the total landfilled carbon stocks for a given year, the tool employs: (1) the
composition of the yard trimmings; (2) the mass of yard trimmings and food scraps
discarded in landfills; (3) the carbon storage factor of the landfilled yard trimmings and food
scraps adjusted by mass balance; and (4) the rate of decomposition of the degradable
carbon.

Due to the number of factors involved, the Landfilled Yard Trimmings and Food Scraps
sector worksheet is arranged by a series of steps. To complete this sector worksheet, follow
the steps below.

1. Enter the amount of landfilled yard trimmings and food scraps.

a.	Enter the composition of yard trimmings in the orange cells as a percent of
grass, leaves, and branches. Default percentages are available by clicking on
the check boxes to the right of the orange input cells and are provided by
Oshins and Block (2000). Figure 12 displays the inputs cells where this
information is entered. If the user-specific inputs do not match the default
data in the worksheet (i.e., the default value is overwritten), the text will
appear red.

b.	Enter the total annual landfilled yard trimmings and food scraps from 1960 to
the present in short tons of wet weight in the yellow input cells. Default data
are provided by clicking on the gray "Use default yard trimmings data" button
above the yellow input cells. The tool uses the percentage entered for yard
trimmings in the previous step to allocate the amount of yard trimmings
distributed among grass, leaves, and branches. The default data from U.S.
EPA (2020) is a national total for yard trimmings and food scraps and is
distributed to each state based on state population U.S. Census Bureau
(2021).

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.17

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Figure 12. Landfilled Yard Trimmings and Food Scraps Worksheet, Step 1

6. Landfilled Yard Trimmings and Food Scraps in California

Estimates of net carbon flux of landfilled yard trimmings and food scraps can be calculated by estimating the change in landfill
carbon stocks between inventory years. To determine the total landfilled carbon stocks for a given year, the following factors
are estimated: (1) the composition of the yard trimmings, (2) the mass of yard trimmings and food scraps discarded in the
state's landfills, (3) the carbon storage factor of the landfilled yard trimmings and food scraps, and 4) the rate of decomposition
of the degradable carbon. The amount of carbon remaining in the landfill for each year is tracked based on a model of carbon
fate that employs the equation outlined in Step 3 below.

Due to the complexity of these calculations, more detail about the methodology is provided below. Please note that many of the
default factors are based on national values that may vary from state to state. States are encouraged to use state-specific data
when available. For more information, please consult the Land Use, Land-Use Change, and Forestry Chapter of the User's
Guide.

Return to
Control Sheet

1. Enter the composition of yard trimmings, and the amount of annually landfilled ya

Content of yard trimmings Default

% Grass 30.3%

% Leaves 40.1%

% Branches 29.6%

Check — must add up to 100% in order to continue:

Percent grass, leaves,
and branches in yard
trimmings

Must equal 100%

Landfilled yard trimmings and scraps, '000 short tons, wet weight

Default landfilled yard trimmings and food scraps = state population x national landfilled yard trimmings and food
Default grass, leaves, and branches = total landfilled yard trimmings x percentages entered above

Use default yard trimmings data

Clear Data

Total landfilled yard trimmings

Leaves
Branches
Food scraps

Total landfilled yard
trimmings and food
scraps, 1960 to present

2. Calculate the amount of carbon added to landfills annually.

a. Enter the initial carbon content percent for grass, leaves, branches, and food
scraps in the orange cells, as shown in Figure 13. The default percentages
are taken from Barlaz (1998). If the user-specific inputs do not match the
default data in the worksheet (i.e., the default value is overwritten), the text
will appear red.

b. Enter the dry weight to wet weight ratio for grass, leaves, branches, and food
scraps, also shown in Figure 13. This default information is drawn from
Tchobanoglous, et al. (1993). If the user-specific inputs do not match the
default data in the worksheet (i.e., the default value is overwritten), the text
will appear red.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.18

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Figure 13. Landfilled Yard Trimmings and Food Scraps Worksheet, Step 2

6. Landfilled Yard Trimmings and Food Scraps in California

Estimates of net carbon flux of landfilled yard trimmings and food scraps can be calculated by estimating the change in landfill
carbon stocks between Inventory years. To determine the total landfilled carbon stocks for a given year, the following factors
are estimated: (1) the composition of the yard trimmings, (2) the mass of yard trimmings and food scraps discarded in the
state's landfills, (3) the carbon storage factor of the landfilled yard trimmings and food scraps, and 4) the rate of decomposition
of the degradable carbon. The amount of carbon remaining in the landfill for each year is tracked based on a model of carbon
fate that employs the equation outlined in Step 3 below.

2. Calculate the amount of carbon added to landfills annually
Key Assumptions

Initial Carbon Content

Grass
Leaves
Branches
Food Scraps

Dry Weight/Wet Weight ratio

Grass
Leaves
Branches
Food Scraps

Default

44.9%
45.5%
49.4%
50.8%

Default

30.0%
70.0%
90.0%
30.0%

^SC default? | Use Default Percent for

(Mjfbk for Ves)

Enter initial carbon
contents.

Return to
Control Sheet

Clear All Data

Enter dry weight to wet
weight ratio.

Total Mass Additions. '000 metric tons C

Mass additions of carbon = landfilled materials, wet weight x initial carbon content x dry weight/wet weight ration x metric tons per short ton

3. Calculate the total annual stocks of landfilled carbon.

a. In the orange input cells, enter the proportion of carbon from each material
stored in landfills indefinitely, as shown in Figure 14. Or use the default
proportions, based on Barlaz (1998, 2005, and 2008). If the user-specific
inputs do not match the default data in the worksheet (i.e., the default value
is overwritten), the text will appear red.

b. Enter the half-life of the degradable carbon in each of the materials in years,
shown in Figure 14. The default data are from IPCC (2006). If the user-
specific inputs do not match the default data in the worksheet (i.e., the
default value is overwritten), the text will appear red.

Once this sector worksheet is complete, use the gray navigational arrow to return to the
control worksheet.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.19

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Figure 14. Landfilled Yard Trimmings and Food Scraps Worksheet, Step 3

A B C D E F G

6. Landfilled Yard Trimmings and Food Scraps in California

Estimates of net carbon flux of landfilled yard trimmings and food scraps can be calculated by estimating the change in landfill
carbon stocks between Inventory years. To determine the total landfilled carbon stocks for a given year, the following factors
are estimated: (1) the composition of the yard trimmings, (2) the mass of yard trimmings and food scraps discarded in the
state's landfills, (3) the carbon storage factor of the landfilled yard trimmings and food scraps, and 4) the rate of decomposition
of the degradable carbon. The amount of carbon remaining in the landfill for each year Is tracked based on a model of carbon
fate that employs the equation outlined in Step 3 below.

3. Calculate the total annual stocks of landfilled carbon

Enter proportion of carbon
stored permanently

Return to
Control Sheet

Clear All Data

Proportion of Carbon Stored
Permanently

Grass
Leaves
Branches
Food Scraps

Half-life of degradable carbon
(years)

Grass
Leaves
Branches
Food Scraps

Use Default Percent for All?

Default

53.5%
84.6%
76.9%
15.7%

Default

20
23.1
3.8

r i

Enter half-life of
degradable carbon

Use»lW[

(CmUFfor Yes)

r i
n
r i

Total Stocks of Landfilled Carbon, '000 metric tons C

Annual carbon stocks are calculated by summing the carbon remaining from all previous years' deposits of waste.

The stock of carbon remaining in landfills from any given year is calculated as follows:

Initial C Addition x (Proportion of C Stored Permanently + (1 - Proportion of C Stored Permanently) x e *(-ln(0.5)/half-life of degradable C))

To calculate stocks for any given year, the remaining stocks for all previous years are summed.

The table below provides a summary of the calculated annual C stored in landfills. To view the more detailed calculations for each year, click on the navigational arrow below.

Step (7) Select an Option for Agricultural Soil Carbon Flux
Control Worksheet

The control worksheet allows you to either select the default data provided or to enter user-
specified data to be used throughout the tool. To proceed with the default data, select the
first radio button under step 7 on the control worksheet. If you would like to use your own
state-specific data, select the second radio button under step 7 of the control worksheet.
See Figure 15 for an example of the radio buttons in step 7.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.20

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Module 8 - Land Use, Land-Use Change, and Forestry Module January 2022

Figure 15. Control Worksheet for the LULUCF Module

52 7. Agricultural Soil Carbon Flux (in Cropland and Grassland soils)

^ Click here if you do not have any data on carbon flux in agricultural soils and would like to use default estimates
from the U.S. EPA's Inventory of Greenhouse Gas Emissions and Sinks: 1990-2015.

<5o to Agricultural Soil
Carbon Flux Sheet

»oil\.

O Click here if you would like to use your own data for agricultural soil carbon flux.

56 8. Continue to estimate emissions . . .

Agricultural Soil
Carbon Flux Radio
Buttons

67
&&.

9. Export the results for use in the Synthesis Tool.

Go to Summary
Sheet

Export data

Carbon is continuously cycled through the cropland and grassland ecosystems and the
atmosphere. The amount of carbon stored in cropland varies according to crop type,
management practices (e.g., rotation, tillage, drainage), and soil and climate variables. The
amount of carbon stored in grassland depends on management practices (e.g., irrigation)
and is also impacted by inter-annual climate variability, such as increased rainfall (IPCC
2006). Soil is the primary carbon pool in both cropland and grassland (U.S. EPA 2021).

The net change in agricultural soil carbon is the change in the amount of carbon stored
primarily in mineral and organic soils over time. This section presents the methodology for
calculating agricultural soil carbon flux.

After completing the control worksheet for this sector, use the gray arrows to navigate to
the Agricultural Soil Carbon Flux worksheet.

Agricultural Soil Carbon Flux Worksheet

If you are using the default data for agricultural soil carbon flux estimates, there is no
further information to enter. Figure 16 shows the default agricultural soil carbon worksheet.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.21

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Figure 16. Example of Agricultural Soil Carbon Flux Worksheet Using Default Data

If you are using your own data on agricultural soil carbon flux, in the red cells enter total
carbon flux data for cropland and grasslands (including land recently converted to cropland
and grassland). Figure 17 shows the worksheet where you will enter agricultural soil carbon
flux data. Once this sector worksheet is complete, use the gray navigational arrow to return
to the control worksheet and proceed to the next step.

Figure

7. Example of User-Entered Data Agricultural Soil Carbon Flux Worksheet

ar [cultural Soil Carbon Flux in California

Click here to find
possible data

1



?



J

8



9

10



11

1990

13

1991

15

1992

17

1993

19

1994

21

1995

23

1996

25

1997

27

1998

29

1999

31

2000

33

2001

35

2002

37

2003

39

2004

41

2005

43

2006

Enter net sequestration as a negative value, net emissions as a positive value in million metric tons of carbon dioxide
equivalent. To use default data from U.S. EPA's Inventory of Greenhouse Gas Emissions and Sinks:1990-2016,
select the appropriate option in Step 9 on the control worksheet.

Total

MMTCOsE (million metric tons of carbon
dioxide equivalent)

Enter flux data in red cells

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.22

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Step (8) Review Summary Information

The steps above provide estimates of total emissions and sequestration from land use, land-
use change, and forestry activities. The information from each sector worksheet is collected
on the summary worksheet, which displays results in MMTCO2E. Figure 18 shows the
summary worksheet that sums the emissions and sinks from all components of the LULUCF
module. In addition, the results are displayed in graphical format at the bottom of the
summary worksheets. Depending on whether the user entered their own data for forest
carbon flux or used the default data provided by the module, additional rows may be shown
to summarize emissions totals from Forest Land Remaining Forest Land, Land Converted to
Forest Land, and Forest Land Converted to Land.

Figure 18. Example of the Emissions Summary Worksheet in the LULUCF Module

8. Summary of Land Use, Land-Use Change, and Forestry Emissions and
Sequestration for California

Note: The Land Use, Land-Use Change, and Forestry module no longer estimates carbon dioxide emissions from Liming of Soils and Urea Fertilization. These categories are now
estimated in the Agriculture module.

Emissions were not calculated for the following sector: Forest Fires. If you skipped any of these by mistake, please return to the control worksheet and complete each skipped source.	

Emissions* (AAAATCO2E)



1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

Forest Carbon Flux

(54.54)

(54.29)

(54.05)

(50.04)

(49.78)

(49.53)

(49.27)

(49.02)

(48.77)

(48.51)

(48.26)

(48.01)

Aboveground Biomass

(28.59)

(28.35)

(28.11)

(27.87)

(27.64)

(27.42)

(27.19)

(26.97)

(26.74)

(26.52)

(26.29)

(26.07)

Belowground Biomass

(6.28)

(6.23)

(6.18)

(6.12)

(6.08)

(6.03)

(5.98)

(5.93)

(5.88)

(5.83)

(5.78)

(5.73)

beadwood

(5.68)

(5.72)

(5.76)

(5.79)

(5.82)

(5.84)

(5.87)

(5.89)

(5.91)

(5.94)

(5.96)

(5.99)

Litter

(0.38)

(0.37)

(0.37)

(0.36)

(0.36)

(0.36)

(0.36)

(0.35)

(0.35)

(0.35)

(0.35)

(0.34)

Soil (Mineral)

0.61

0.60

0.58

0.57

0.57

0.57

0.57

0.58

0.58

0.58

0.58

0.58

Soil (Organic)

(0.00)

(0.00)

(0.00)

(0.00)

(0.00)

(0.00)

(0.00)

(0.00)

(0.00)

(0.00)

(0.00)

(0.00)

brained Organic Soil

























Total wood products and landfills

(14.22)

(14.22)

(14.22)

(10.46)

(10.46)

(10.46)

(10.46)

(10.46)

(10.46)

(10.46)

(10.46)

(10.46)

Urban Trees

(4.66)

(4.74)

(4.82)

(4.90)

(4-98)

(5.06)

(5.14)

(5.22)

(5.30)

(5.37)

(5.45)

(5.47)

Landf illed Yard Trimmings and Food Scraps

(2.94)

(2.80)

(2.77)

(2.42)

(2.12)

(1.74)

(1.44)

(1.53)

(1.52)

(1.43)

(1.42)

(146)

Grass

(0.24)

(0.22)

(0.22)

(0.17)

(0.14)

(0.10)

(0.06)

(0.06)

(0.07)

(0.06)

(0.06)

(0.07)

Leaves

(1.18)

(1-14)

(1.13)

(0.98)

(0.87)

(0.73)

(0.60)

(0.58)

(0.56)

(0.52)

(0.49)

(0.51)

Branches

(1.18)

(1.13)

(1-12)

(0.97)

(0.85)

(0.71)

(0.58)

(0.55)

(0.54)

(0.49)

(0.46)

(0.48)

Landf illed Food Scraps

(0.34)

(0.30)

(0.31)

(0.29)

(0.26)

(0.21)

(0.20)

(0.33)

(0.35)

(0.36)

(0.41)

(0.41)

Forest Fires
CHt
NzO

























NjO from Settlement Soils

0.23

0.22

0.21

0.23

0.23

0.26

0.28

0.24

0.22

0.25

0.27

0.30

Agricultural Soil Carbon Flux

(3.46)

(3.95)

(3.36)

(2.12)

(4.65)

(3.00)

(5.05)

(3.72)

(4.38)

(5.14)

(7.51)

(7.04)

Total

(6S.36)

(65.56)

(64.79)

(59.24)

(61.29)

(59.07)

(60.61)

(59.25)

(59.74)

(60.21)

(62.37)

(61.69)

* Note that parentheses indicate net sequestration

























Return to Control
Sheet

Review discussion of
uncertainty associated with
these results

Step (9) Export Data

The final step is to export the summary data. Exporting data allows the estimates from
each module to be combined later by the Synthesis Module to produce a comprehensive
GHG inventory for the state.

To access the "Export Data" button, return
to the control worksheet and scroll down to
the bottom (9). Click on the "Export Data"
button and a message box will open that
reminds the user to make sure all steps of
the module have been completed. If you
make any changes to the LULUCF module
later, you will then need to re-export the
results.

Note: the resulting export file should not be
modified. The export file contains a summary
worksheet that allows users to view the results, as well as
a separate data worksheet with an unformatted version of
the results. The second worksheet, the data worksheet,
contains the information that is exported to the Synthesis
Tool. Users may not modify that worksheet.
Adding/removing rows, moving data, or making other
modifications jeopardize the ability of the Synthesis
Module to accurately analyze the data.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.23

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Clicking "OK" prompts you to save the file. The file is already named, so you only need to
choose a convenient place to save the file. After the file is saved, a message box will
appear indicating that the data was successfully exported.

While completing the modules, you are encouraged to save each completed module; doing
so will enable you to easily make changes without re-running it entirely.

Following data export, the module may be reset and run for an additional state.
Alternatively, you may run the remaining modules of the SIT to obtain a comprehensive
profile of emissions for your state.

1.4 Uncertainty

In the upper right-hand corner of the summary worksheet is a button: "Review discussion of
uncertainty associated with these results." By clicking on this button, you are taken to a
worksheet that discusses the uncertainty surrounding the activity data and emission factors,
and how the uncertainty estimates for this source category affect the uncertainty of the
emission estimates for your state.

1.5 References

Barlaz, M.A. 2008. Corrections to Previously Published Carbon Storage Factors. In a letter
report to Randy Freed of ICF International. February 28, 2008.

Barlaz, M.A. 2005. "Decomposition of Leaves," letter report to Randy Freed of ICF
International, June 29, 2005.

Barlaz, M.A. 1998. "Carbon Storage during Biodegradation of Municipal Solid Waste

Components in Laboratory-Scale Landfills." Global Biogeochemical Cycles 12: 373-380.

Domke, Grant M.; Walters, Brian F.; Nowak, David J.; Smith, James, E.; Ogle, Stephen M.;
Coulston, J.W.; Wirth, T.C. 2021. Greenhouse gas emissions and removals from forest
land, woodlands, and urban trees in the United States, 1990-2019. Resource Update FS-
227. Madison, WI: U.S. Department of Agriculture, Forest Service, Northern Research
Station. 5 p. https://www.nrs.fs.fed.us/pubs/62418.

IPCC. 2006. 2006 IPCC Guidelines for National Greenhouse Gas Inventories, Volume 4:
Agriculture, Forestry, and Other Land Use. The National Greenhouse Gas Inventories
Programme, The Intergovernmental Panel on Climate Change. [H.S. Eggleston, L.
Buendia, K. Miwa, T. Ngara, and K. Tanabe (eds.)]. Hayama, Kanagawa, Japan.

IPCC. 2003. Good Practice Guidance for Land Use, Land-Use Change, and Forestry. J.
Penman and others, editors. IPCC National Greenhouse Gas Inventories Programme.
Available online at http://www.ipcc-nggip.iges.or.jp/public/gpglulucf/gpglulucf.htm.

Nowak, D.J., E.J. Greenfield, R.E. Hoehn, and E. Lapoint. 2013. Carbon Storage and
Sequestration by Trees in Urban and Community Areas of the United States.
Environmental Pollution 178: 229-236. March 12, 2013.

Nowak, D.J. and E.J. Greenfield. 2012. Tree and impervious cover in the United States.
Journal of Landscape and Urban Planning (107) pp. 21-30.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module 1.24

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Module 8 - Land Use, Land-Use Change, and Forestry Module

January 2022

Nowak, D.J., J.T. Walton, L.G. Kaya, and J.F. Dwyer. 2005. "The Increasing Influence of
Urban Environments on U.S. Forest Management." Journal of Forestry 103(8):377-382.

Oshins, C., and D. Block. 2000. "Feedstock Composition at Composting Sites." Biocycle

41(9):31-34.

Smith, J. 2014. Estimates of Forest Carbon Stocks and Flux: 1990-2014. E-mail

correspondence between ICF and Jim Smith, USDA Forest Service. October 1, 2014 and
January 27, 2015.

Smith, W. Brad; Vissage, John S.; Darr, David R.; Sheffield, Raymond M. 2001. Forest
Resources of the United States, 1997. Gen. Tech. Rep. NC-219. St. Paul, MN: United
States Department of Agriculture, Forest Service, North Central Research Station. 190 p.

Tchobanoglous, G., H. Theisen, and S.A. Vigil. 1993. Integrated Solid Waste Management,
1st edition. McGraw-Hill, NY. Cited by Barlaz (1998).

U.S. Census Bureau. 2021. National Population Totals and Components of Change: 2010-
2019. U.S. Census Bureau, Washington, DC. Available online at:
http://www .census, gov.

U.S. Census Bureau. 2012. Census 2010 Urbanized Area and Urban Cluster Information.
Available at: https://www2.census.aov/aeo/docs/reference/ua/ua st list all.txt.

U.S. Census Bureau. 2002. Census 2000 Urbanized Area and Urban Cluster Information.
Available at: https://www.census.aov/aeo/reference/ua/urban-rural-2000.html.

U.S. Census Bureau. 1990. Census 1990 Urbanized Area and Urban Cluster Information.

U.S. EPA. 2020. Advancing Sustainable Materials Management: Facts and Figures for 2018.
United States Environmental Protection Agency, Washington, DC. Available at
https://www.epa.qov/facts-and-fiaures-about-materials-waste-and-recvclinq/advancinq-
sustainable-materials-manaaement.

U.S. EPA. 2021. Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990 - 2019.

Office of Atmospheric Programs, U.S. Environmental Protection Agency. EPA 430-R-21-
005. Available at: https://www.epa.qov/qhqemissions/inventorv-us-qreenhouse-qas-
emissions-and-sinks-1990-2019.

U.S. EPA. 2003. Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990 - 2001.

Office of Atmospheric Programs, U.S. Environmental Protection Agency. Available at:
https://www.epa.qov/qhqemissions/inventorv-us-qreenhouse-qas-emissions-and-sinks-
1990-2001.

State Greenhouse Gas Inventory Tool User's Guide for the Land Use, Land-Use Change, and
Forestry Module	1.25

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