CED User Manual V2.0.0 (2017.10.24)

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SAGEBRUSH
CONSERVATION EFFORTS DATABASE
User Manual
Version 2.0.0

A Living Document That Will Be Refined With Use
U.S. Fish and Wildlife Service
October 24, 2017
CED User Manual 2.0.0 Please check https://conservationefforts.org for updates

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TABLE OF CONTENTS
CONSERVATION EFFORTS DATABASE EXECUTIVE SUMMARY ...................................................................... 4
1.0 CED DATA PROVIDERS............................................................................................................................. 7
1.1 CED Data Providers ............................................................................................................................. 7
1.2 CED Privacy and Transparency ............................................................................................................ 7
2.0 CED CONTENTS AND STRUCTURE ........................................................................................................... 8
2.1 Implementation and Effectiveness Information ................................................................................. 9
2.2 Plan Information ............................................................................................................................... 12
2.2.1 Regulatory Mechanisms, Plans, and Policies ............................................................................. 14
2.2.2 Incentive-based (Non-regulatory) Conservation Strategies ...................................................... 14
2.3 Project Information ........................................................................................................................... 15
2.3.1 Mitigation ................................................................................................................................... 15
2.3.2 Activities, Subactivities, and Metrics ......................................................................................... 15
3.0 HOW WILL DATA IN THE CED BE USED? ............................................................................................... 21
4.0 REPORTING ........................................................................................................................................... 21
5.0 PROJECT SITING..................................................................................................................................... 21
6.0 INTEROPERABILITY ................................................................................................................................ 22
7.0 ENTERING DATA IN THE CED ................................................................................................................. 22
7.1 Individual Plan and Projects .............................................................................................................. 23
7.2 Batch Uploads ................................................................................................................................... 24
7.3 Geospatial Data ................................................................................................................................. 24
7.4 Getting Started.................................................................................................................................. 24
7.4.1 Welcome Page ........................................................................................................................... 25
7.5 Register for an Account..................................................................................................................... 26
7.6 Enter Profile Information .................................................................................................................. 26
7.7 Create a New Project/Plan ................................................................................................................ 28
7.8 Entering a Conservation Effort.......................................................................................................... 28
7.8.1 SPATIAL PROJECTS ..................................................................................................................... 28
Step 1: Conservation Effort Name & Completion Status .................................................................... 28
Footprint Editor – Spatial Data Upload and Digitizing ........................................................................ 30

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Step 2: Location Information .............................................................................................................. 31
Step 3: Implementation and Effectiveness Information ..................................................................... 33
Step 4: Activity Information ................................................................................................................ 34
Documentation ................................................................................................................................... 34
Step 5: Review and Submit Your Conservation Effort ........................................................................ 37
7.8.2 NON-SPATIAL PROJECTS ............................................................................................................ 39
Step 1: Conservation Effort Name & Completion Status .................................................................... 39
Step 2: Location Information .............................................................................................................. 41
Step 3: Implementation and Effectiveness Information ..................................................................... 42
Step 4: Activity Information ................................................................................................................ 43
Documentation ................................................................................................................................... 44
Step 5: Review and Submit Your Conservation Effort ........................................................................ 45
7.8.3 PLANS ......................................................................................................................................... 47
Step 1: Conservation Effort Name & Completion Status .................................................................... 47
Step 2: Location Information .............................................................................................................. 48
Step 3: Implementation and Effectiveness Information ..................................................................... 49
Step 4: Activity Information ................................................................................................................ 50
Documentation ................................................................................................................................... 51
Step 5: Review and Submit Your Conservation Effort ........................................................................ 52
8.0 NEXT STEPS ........................................................................................................................................... 54
9.0 VIEW AND EDIT A PROJECT/PLAN ......................................................................................................... 54
10.0 DELETE A PROJECT/PLAN .................................................................................................................... 54
11.0 BATCH UPLOAD ................................................................................................................................... 55
12.0 INTERACTIVE MAP and REPORTING.................................................................................................... 55
13.0 RECORD QUERY ................................................................................................................................... 56
14.0 SUBMIT A BUG REPORT ...................................................................................................................... 56
15.0 ASK A QUESTION ................................................................................................................................. 56
APPENDIX A – Glossary ................................................................................................................................. 1
APPENDIX B – Proposed Uses/Analyses for Data Collected ......................................................................... 1
APPENDIX C – Literature Cited ...................................................................................................................... 1

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CONSERVATION EFFORTS DATABASE EXECUTIVE SUMMARY
The sagebrush ecosystem is the largest ecosystem type in the continental U.S., providing habitat for
more than 350 associated fish and wildlife species. In recognition of the need to conserve a healthy
sagebrush ecosystem to provide for the long-term conservation of its inhabitants, the US Fish and
Wildlife Service (Service) and United States Geological Survey (USGS) developed the Conservation Efforts
Database version 2.0.0 (CED). The purpose of the CED is to efficiently capture the unprecedented level
of conservation plans and actions being implemented throughout the sagebrush ecosystem and
designed to capture actions not only for its most famous resident, the greater sage-grouse (Centrocercus
urophasianus; hereafter, sage-grouse) but for the other species that rely on sagebrush habitats.
The Service completed a range-wide status review of the greater sage-grouse in September 2015,
resulting in a ‘not warranted’ finding, under the Endangered Species Act (ESA). As part of that status
review, the Service evaluated a combination of voluntary, incentive-based efforts, habitat restoration
projects, and management through regulatory mechanisms. The Service used the Conservation
Objectives Team final report (COT report; USFWS 2013), and the threats described therein, as guidance
to identify the conservation actions that would address and reduce the threats and/or the associated
impacts. After coordinating and collaborating with State and Federal partners, a list of conservation
actions to address and ameliorate those threats was generated for use in the CED.
The Service will continue to work collaboratively with its partners to identify new information to collect
and how to utilize it as we gain new insight on links between conservation efforts and biological
responses to sagebrush habitats as well as resources values for particular species. The Service has made
a commitment to make these adjustments to reflect our shift, and the shift of many of our conservation
partners, to an ecosystem based approach to conservation, as well as to be adaptable and make
changes in the future based on release of new science and information that informs effective
conservation.
While the focus of the CED has shifted to focus on the entire ecosystem, it will continue to serve as the
data collection tool to support analyses and inform any future greater sage-grouse status reviews,
including but not limited to the 2020 status review described in the 2015 federal register document (80
FR 59857).
The CED is easy to use. This is a web-based database with a geospatial component that is used to collect
information on the plans and projects currently being implemented, or with a high likelihood of being
implemented in the near future, to conserve sagebrush habitats as well as the species dependent on
them (i.e. sage-grouse, Brewer’s sparrow, etc.). Developed to provide a secure and transparent way to
gather information on sagebrush conservation efforts, the CED allows multiple users to enter
information about their conservation efforts and link them to one or more threats to a species.
Conservation plans, individual project descriptions and reports, tabular data from large data sets, spatial
data, and documentation of data sources can all be entered in the CED, which is housed on the data
sharing platform, Landscape Conservation Management and Analysis Portal (LC MAP). LC Map is
managed by the Great Northern Landscape Conservation Cooperative (GNLCC). The CED is user-friendly
for all technical levels and was designed with efficiency in mind. No GIS skills are required for entering
data on individual plans or projects, and USGS programmers are available to help with batch uploads of
large data sets or GIS files.

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The CED is secure. Agencies and organizations will work with the Service/USGS CED Team to establish
approving officials to determine who can enter and edit data in the CED for their organization. These
agency-designated approving officials will also allow for important oversight of data entry and QA/QC.
The CED is transparent. The information on the CED will become part of the public record and may be
publicly disclosed as part of the Service’s administrative record or in response to a request under the
Freedom of Information Act (FOIA). Additionally, we offer users the option to make their data readily
available to anyone, or to a subset of registered users of their choosing.
The CED is simple. Each project or plan entry consists of six main components:
1. Basic project information
2. Location information (easy-to-use onscreen digitize*, upload shapefiles*, and in some cases,
selection of ‘canned’ areas of interest (States, Counties, etc.).
3. Activities, subactivies, and metrics*
4. Objectives* and likely effects* of the activity
5. Threats addressed
6. Uploading supporting documents
7. Information describing implementation and [biological] effectiveness*
* Some components are only required for specific activities and subactivities
How will the information be used? Each plan or project/treatments entered in the CED will be linked to
one or more of the following thirteen threats (in alphabetical order) identified in the COT report (USFWS
2013) as well as areas of interest relevant to sage-grouse. As we gain better understanding of the
threats contributing to habitat loss, fragmentation and degradation in the sagebrush ecosystem, some
of these threats and conservation actions aimed at reducing or eliminating their impacts, we will adjust
accordingly in an effort to better represent the potential benefit of the action implemented.
•
•
•
•
•
•
•
•
•
•
•
•
•

Agricultural Conversion
Conifer Encroachment
Energy Development
Fire
Free-Roaming Equids (Feral Horses and Burros)
Improper Grazing/Range Management
Infrastructure
Isolated/Small Population Size
Mining
Noxious Weeds/Annual Grasses
Recreation
Sagebrush Elimination
Urban Development

We will review the information about individual projects and plans entered into the CED to evaluate the
extent to which these efforts will reduce or eliminate the threats to sagebrush habitats (and species
dependent on them) identified in the COT report (USFWS 2013), with the goal of compiling these results
to generate a range-wide assessment of sage-grouse and sagebrush conservation efforts. The CED does
not collect information about the distribution or severity of threats to sagebrush (or sage-grouse); that
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information will be compiled separately by the Service and available for viewing when using the CED’s
Interactive Map. However, some threat information will be displayed in the background of the CED (and
the Interactive Map) to aid in the evaluation of conservation efforts.
An overview of some of the basic components of the CED is provided in Fig. 1. This schematic is not allinclusive, but provides general information on the structure of the database. For more information,
please visit https://conservationefforts.org

Figure 1. Simplified portrayal of the CED structure and information flow.

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1.0 CED DATA PROVIDERS
Conservation partners throughout the sagebrush biome, spanning 13 states and 2 provinces, are
undertaking unprecedented actions to conserve sagebrush (and sage-grouse) habitats. These
conservation actions include, but are not limited to: landscape-scale Federal and State management
plans that provide regulatory mechanisms, incentives, and/or strategic approaches to conserve
important sage-grouse habitat as well as on-the-ground habitat restoration projects such as addressing
piñon-juniper encroachment, improving wet meadow habitats, and restoring habitat loss to fire for the
conservation of sage-grouse habitats.
An important element of our long-term monitoring will be a compilation of the conservation efforts
currently being implemented, or planned for implementation in the near future, to conserve sagebrush
habitats and the species dependent on them. The CED was developed to collect this information from
partners in a standardized way so that we can assess the distribution of various types of conservation
activities and evaluate their effectiveness in reducing or eliminating threats across the ecosystem. This
standardized way of collecting information related to conservation efforts will allow the Service to work
with our partners to monitor, long-term, the benefits realized through effective implementation of
conservation efforts.

1.1 CED Data Providers
Federal agencies, State agencies, Tribal governments, local governments, non-governmental
organizations (NGOs) members of industry, universities, and others will all be able to enter information
describing their conservation efforts in the CED.
Data providers are asked to enter information describing
the conservation plans and projects/treatments they have
implemented or developed that will conserve sagebrush
habitats and associated species, and also provide
information on the implementation and effectiveness of
those conservation efforts. Section 2.2 and 2.3 provide
more detailed information on the elements of those three
components.

Projects vs. Treatments
For the purposes of this document, the
terms ‘projects’ and ‘treatments’ are
used in a general sense. We discuss how
to report spatial information associated
with efforts in Section 7.

1.2 CED Privacy and Transparency
All data in the CED will become part of the public record and may be publicly disclosed as part of the
Service’s administrative record or in response to a request under the Freedom of Information Act (FOIA).
All interested persons (general public) will be able to view a scalable map of all conservation efforts
entered in the CED. An example is provided in Figure 2. The finest viewable scale will be set at 1 inch =
1 mile. This synoptic map will provide an overview of the database contents and potentially generate
further interest in local restoration and conservation efforts. The Interactive Map will also aid in coarsescale siting of potential conservation efforts (see Section 5.0). A polygon (and in limited cases, a point)
on the map will represent a conservation effort, also known as a ‘database record’, for that location.

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The following information will be visible to any database user for each conservation effort, or record, on
the map:
•
•
•
•
•

Effort ID Number
Effort Name
Subactivity
Total acres (and in some limited cases, ‘total miles’)
Implementing party and contact information

Figure 2. Sample Map Viewable by Public

Registered CED users that provide data in the CED will be able to generate reports and maps for the data
that they have provided. At this time, no users of the CED other than the Service may generate
comprehensive reports from multiple database records; however, the Service is exploring options to
make some information readily available. However, all interested individuals or parties will be able to
contact any implementing party to request additional information about a plan or project. If a CED data
provider wants information in the CED that was provided by a different CED data provider, they need to
obtain that information directly from the data owner. This will provide security for CED data providers
and allow for them to communicate directly with those requesting additional information and provide
responses to those requests.

2.0 CED CONTENTS AND STRUCTURE
The CED is focused on collecting information on conservation efforts that have been implemented after
2009 and those conservation efforts that have a high likelihood of being implemented in the near
future. If conservation partners have data on significant conservation efforts that were not provided or
were not yet effective prior for the 2010 finding, the CED will accept data prior to 2009, and we
encourage you to work with the CED to get that information uploaded. Some of that information may
have been collected as part of the data call for the 2015 greater sage-grouse status review; however, no
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information was entered into the database after February, 2015. The CED will be ‘open’ beginning in
October, 2017 and will remain open. The Service has the ability to use a ‘snapshot’ of the data provided
at any time, and this will hopefully preclude or reduce the need to have a concentrated data call for any
potential future actions as well as preclude the CED from needing to be ‘closed’ during any analysis.
The CED is designed to capture conservation efforts that will help reduce or eliminate the impacts
associated with threats or otherwise improve the sagebrush habitats. As defined in the Policy for
Evaluation Conservation Efforts (PECE Policy; 68 FR 15100, April 28, 2003), conservation efforts
include plans such as conservation agreements, conservation plans, management plans, and
specific actions to implement those plans (such as juniper removal projects, wet meadow
restoration, and restoration of habitats lost to fire). Activities such as conducting population
surveys, mapping habitat, monitoring plans, public outreach, and holding meetings of local
working groups to design projects, while important, are not intended for entry in the CED.
Each CED record identifies an effort type, activity, subactivity, and one or more threats to provide a
structure for organizing information about sagebrush conservation efforts. Project efforts also identify
quantifiable metrics such as acres (or potentially ‘miles’ in some limited cases) of habitat restored.
Individual subactivities or metrics listed, whether related to an on-the-ground effort or related
regulatory mechanism/plan, are not necessarily applicable everywhere as the threats impacting
sagebrush vary across the landscape in presence and intensity. There are no implications for not
reporting data that does not apply to, or is not available for, each conservation partner. However, some
fields are required, and failure to provide that information may result in a record not being accepted in
the CED. The Service has worked to reduce any fields that are not essential for summary, quantification,
or evaluation of a given record.

2.1 Implementation and Effectiveness Information
The Service will need some basic information about the plan or project entered into the CED to
determine if the plan or project has been fully implemented and if it has been demonstrated to be
effective in addressing one or more threats. Information on the conservation effort objectives and
effectiveness are required for all conservation efforts.
Effort Objectives: In addition to the general project or plan objective(s), the CED is seeking a narrative
explanation of how the effort intends to address one or more threat and/or achieve one or more
conservation objective either identified in the COT Report or otherwise identified as a threat to
sagebrush ecosystems.
For example, a shrub-steppe habitat restoration project may have one or more of the following general
objectives:
•
•
•

Restore key components to enhance habitat quality for sage-grouse.
Restore native bunchgrasses and forbs to an abundance and density that can increase the
resistance of an area to invasives annual grasses.
Restore productive rangelands that also support a diversity of wildlife.

While the above bulleted statements are valid objectives for restoring or improving habitat, the CED
requests that our conservation partners also specify how the achievement of those objectives will help
reduce or eliminate a threat. For example, if the effort objective examples above were achieved, how
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would they reduce impacts from ‘noxious weeds/invasive annual grasses’, and/or minimize ‘wildfire risk’
by reducing invasive annual grasses. Another example is how a conservation easement may not directly
improve sagebrush habitats, but it may ensure that the habitat will not be tilled and converted to
croplands. It will also be helpful if the narrative information in the ‘Objectives’ text box explained how
the effort would accomplish one of the Conservation Objectives outlined on pages 31-52 of the COT
Report if the conservation effort is for sage-grouse, or applies to the species for which the effort is
focused.
Effort Effectiveness: The Service is also seeking information on whether the efforts were successful in
fulfilling the stated treatment objective(s), and effective in ameliorating or reducing one or more threats
to sage grouse. In the CED, three options are available for answering the question: Was the effort
effective?
•
•
•

Yes, the plan or project is already effective.
Highly Likely, the plan or project is reasonably certain to be effective, given adequate time.
Uncertain or Unlikely, plan or project is uncertain, or unlikely, to be effective based on current
information.

In cases where the effort has been deemed effective, or is highly likely to be effective given enough
time, we are seeking narrative information explaining how and why that is the case. If monitoring
reports or other supporting documents are available, we encourage those be uploaded in Step 3.
Restoration of shrub-steppe habitat is a process that takes repeated interventions to control weeds and
restore diverse species assemblages, allow natives to disperse in from adjacent areas, and achieve
compositional and structural objectives. Many variables influence the effectiveness of sagebrush
habitat restoration projects, and it takes many years to achieve functional habitat for associated species.
Recognizing that few, if any, restoration efforts implemented in recent years may have achieved
functional habitat, we encourage partners to report effectiveness based on established incremental
objectives and conducted timely monitoring to demonstrate effectiveness for that point in time. An
example of incremental objectives and effectiveness include:
•
•
•

Year 1 Objective: Greater than 80% of all seeded species will be established on site. Cover of
seeded bunchgrasses will be greater than 15%. Annual weeds will be less than 5% of total
cover. Monitoring indicates these objectives were met.
Year 3: All seeded species will be established. Bunchgrass cover will be greater than 35%.
Annual weeds will be less than 2%. Monitoring was conducted, corrective actions were
implemented to treat annual weed coverage, and all Year 3 objectives were met.
Year 10: Greater than 80% of all species on the reference site species list will be present
within the restoration area. Too early to tell, but based on previous years monitoring and
corrective actions, Year 10 Objectives are highly likely to be met.

If a project contains multiple actions (or treatments), it may be difficult to evaluate each individual
treatment for effectiveness. However, if like treatments are conducted with the same methods, etc.,
those treatments could be evaluated in the aggregate as objectives may be tied to a larger geographic
area. In those cases, we encourage users to group like polygons/efforts for entry into the CED. The
requirements for reporting on effectiveness remain, but this provides flexibility based on the monitoring
strategy and objectives associated with the effort.
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If specific, measurable, time-bound, incremental objectives are not available, other information, such as
the bullets listed below, could help explain why the restoration effort is on the correct trajectory to
provide functional habitat given adequate time:
•
•
•
•
•
•
•

Was the effort part of a broader strategic process that addresses the sagebrush ecosystem
as a whole, and that provides explicit rationale for spatial prioritization of best management
practices to meet the stated objectives?
Were established and proved techniques used for soil prep and seeding rates?
Was periodic weed control provided?
Was herbivore protection in place?
Was there adequate precipitation to establish roots and survive the following summer, or
was supplemental water provided?
Was a follow-up monitoring and a corrective action strategy in place, particularly for sites
with low precipitation, shallow soils, and/or areas with steep, southwest-facing slopes?
Were locally-sourced seeds and/or seedlings used in the restoration effort?

The questions used in the CED to elicit implementation and effectiveness information CED are displayed
in Figure 3.

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Figure 3. Implementation and Effectiveness Information

2.2 Plan Information
The goal for long-term conservation of healthy sagebrush habitats (including native perennial grass and
forb communities) is achieved by maintaining viable, connected, and well-distributed sagebrush
communities through threat amelioration, conservation of key habitats, and restoration activities.
Healthy, viable, connected sagebrush ecosystem in turn provides for viable, connected, and welldistributed populations of sagebrush associated species. One of the objectives to achieve this goal is to
implement state and federal sagebrush conservation strategies (including but not limited to sage-grouse
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conservation strategies and associated incentive-based conservation actions and regulatory
mechanisms.
Recognizing that threats can be ameliorated using a variety of tools within the purview of states and
federal agencies, including incentive-based conservation actions or regulatory mechanisms, the CED
organizes information about planning efforts into two broad categories (Fig. 4).

CED Planning Efforts

Regulatory Plans

Non-regulatory,
volunteer, or incentivebased Plans/programs

Figure 4. Types of Planning Efforts captured in the CED.

We offer the following guidelines for identifying plans for entry in the CED:
Regulatory Plans: Plans with regulatory authority (e.g., laws, regulations, ordinances) that define land
use designations/allocations or control activities that occur in sage-grouse habitat. Examples include
but are not limited to: Federal Land Use Plans, State Management Plans, and County Zoning Ordinances.
Non-regulatory, Volunteer, or Incentive-based Plans: Proactive, voluntary conservation plans that
provide a geospatial prioritization, and/or schedule of implementation for practices and activities
needed for the long-term conservation healthy sagebrush shrubs and native perennial grass and forb
communities and associated species (including sage-grouse). Examples include, but are not limited to:
Programmatic Candidate Conservation Agreements with Assurances (CCAAs), Candidate Conservation
Agreements (CCAs), Programmatic Restoration Plans, and Natural Resources Conservation Service
Strategic Plans. Incentive-based programs can provide a strategic approach for prioritizing opportunities
with landowners.
Fire Suppression Plans: A mix of land use planning efforts and preparation efforts that could be
considered “projects” but for the lack of an on-the-ground component, this planning category is
designed to capture the important fire suppression actions such as geospatial plans to prioritize
fuels management and habitat recovery/restoration designed to improve sagebrush habitats
with greater resistance to invasive annual grasses and/or resilience after disturbances such as
wildfires. This category also includes planning efforts such as agreements to share fire response
resources, or pre-positioning those resources in advance of wildfires.
When entering planning information in the CED, a narrative explanation of what the plan entails
(suggested topics presented below) is required. While not required, we encourage information that
describes implementation and why it is/was effective.
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2.2.1 Regulatory Mechanisms, Plans, and Policies
2.2.1.0 BLM and USFS Federal Land Use Plans
The Bureau of Land Management (BLM) and the U.S. Forest Service (USFS) have developed 15
Environmental Impact Statements that will inform approximately 98 Land Use Plans. For the 2015
greater sage-grouse status review, the National Operations Center (NOC) worked closely with the
Service and USGS CED Team to upload the geospatial data layers of the land use
allocations/designations that are intended to reduce or ameliorate threats to sage-grouse. It is the
Service’s intent to remain in close coordination with the BLM and USFS to ensure that the most up-todate land use allocations/designations are included in the CED.
2.2.1.1 Other Federal, State, Tribal, County, and Local Government Conservation Plans
Because Federal, State, Tribal, county, and local governments manage actions to address multiple
threats, we encourage these partners to enter a separate record for each threat addressed in their
regulatory plans.
We offer the following suggested approach for the threatspecific narratives entered in the CED.
•
•
•
•
•
•

Suggested Naming Convention for
Plans addressing multiple threats:

State: Agency: Plan Name:Fire
Provide basic information as requested
Summarize how the plan addresses the
State: Agency: Plan Name:Mining
suggested objective listed in the COT Report as
applicable.
Summarize policies/regulations/ordinances to
prevent/minimize/ameliorate the threat
Upload relevant documents supporting the summary information provided in Step 2
Check land ownership boxes as appropriate
Implementation information (useful, but not required for plans)
a. Summarize funding source(s) and funding plan
b. Describe any obstacles to full implementation of the plan
c. Describe any successes in implementing the plan
d. Describe implementation plan for the next five years
e. Describe plans for monitoring [biological] effectiveness
f. Include any additional information needed to describe the plan

2.2.2 Incentive-based (Non-regulatory) Conservation Strategies
Incentive-based conservation strategies play an important role in the conservation of sagebrush
associated species, especially on private lands. Because of their conservation potential, programmatic
and/or large scale non-regulatory conservation strategies will be important entries in the CED. Examples
include Voluntary Federal, State, NGO, Local and Tribal habitat restoration programs, Programmatic
Candidate Conservation Agreements, Programmatic Candidate Conservation Agreements with
Assurances, Programmatic Restoration Plans for Invasive Plants, and Programmatic Reclamation Plans.

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2.3 Project Information
2.3.1 Mitigation
Mitigation strategies or programs are designed to avoid, minimize, rectify, reduce over time, and
compensate impacts to sagebrush habitats and the associated species (i.e. the mitigation hierarchy).
Mitigation strategies or programs are typically part of a larger conservation plan or program, and as
such, will be captured in the CED as a regulatory mechanism, plan, or policy. Individual project-specific
minimization or avoidance measures should not be reported as conservation projects in the CED.
However, application of effective minimization and avoidance measures will be important information
to demonstrate the effectiveness of conservation plans. Examples of minimization and avoidance
measures that are part of a broader conservation plan should be described in Step 5 – Implementation
Information for the overall conservation plan.
Individual compensatory mitigation projects can be reported in the CED as project-specific conservation
efforts. Consider the following example: a conservation easement is placed on a ranch with high quality
sage-grouse habitat, protecting that ranch from fragmentation and development threats in perpetuity
as compensatory mitigation for the siting of a new communication tower in general habitat. The
conservation easement would be entered in the CED, whereas any applicable minimization measures
such as construction timing restrictions, or footprint reduction stipulations for the new communication
tower would not be entered in the CED as a specific conservation effort.
2.3.2 Activities, Subactivities, and Metrics
Table 1 provides a list of the quantitative project metrics used in the CED, organized by ‘Activity’ and
‘Subactivity’. A project can only be associated with one activity and one subactivity. In cases where a
conservation effort includes several activities and subactivities (e.g., a comprehensive restoration action
on a land parcel to decommission an old telecommunication road, revegetate that road, and place a
perpetual conservation easement specifically for sage-grouse (or other sagebrush dependent species)
on that parcel), the data provider is encouraged to either enter multiple CED effort records (one for each
sub-activity or action), or to enter the project for the highest conservation value for the area. Please let
the CED Team know if you have multiple projects that include multiple subactivities so we can revisit this
if needed.
Not all relevant information will be captured by the metrics associated with each subactivity; therefore,
in addition to standardized data fields and metrics, qualitative information will be gathered from text
box entries and from supplemental documents that can be uploaded by registered CED users. Narrative
reports, plans, monitoring results, and other documents will provide essential context for information
provided in standardized format and other valuable information about each conservation effort entered
into the CED. This supporting information will be invaluable when evaluating actions for effectiveness.
When and where alike actions have taken place in an area, but may be geographically disjointed, users
are encouraged to ‘lump’ actions together as long as they have the same outcomes, and
support/justification for effectiveness can be applied similarly across all treatment areas. An example of
this would be five conifer removal treatments that occurred in the same project area. If the treatments
share the same methodology, habitat objectives, post-treatment monitoring results, and same
justification of effectiveness, the 5 separate polygons could be combined into one shapefile, and
uploaded as one record as opposed to 5. This bundling is aimed at reduced workload from the
perspective of our partners, and may increase efficiencies in the Service’s evaluation process.
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Table 1. List of spatially-explicit activities, subactivities, and metrics.
ACTIVITY

SUBACTIVITY

EXAMPLES AND INFORMATION TO INCLUDE
(Objectives, Notes, Effectiveness Narrative Boxes)

PROJECT METRICS
Acres in the Agreement

•

Length of agreement
Conservation
Easement

•

(years, perpetuity)

Early termination penalty
•
SAGEBRUSH
PROTECTION:

Land Acquisition

(yes/no)

•
•

Acres
•

Fuel Breaks

Acres of Fuel Break(s)

Long-term or permanent easements such as those provided
through the Grassland Reserve Program, Farm and Ranchlands
Protection Program, Wetland Reserve Program, and the 2014
Farm Bill Agricultural Conservation Easement Program, or
provided through other Federal, State, or NGO programs.
Please be sure to redact any PII from the information
provided.
Permanent protections such as acquisitions of lands for
governmental or NGO programs where the purpose is for
sagebrush habitat wildlife dependent species.
Fuel breaks involve removing flammable vegetation in a swath
wide enough to prevent a fire from spreading. Roads and
natural fuel breaks can sometimes be incorporated into the
design. If the project or plan has reduced the threat of wildfire
by creating fuel breaks as a habitat protection measure, please
provide a summary in which you respond to the following
questions: what type of fire break(s) was/were created? What
was the reason for the siting/placement of the firebreak? How
will the firebreak be maintained?

Projects to remove piñon pine and/or juniper in all phases.
•
RESTORATION:
Conifer Removal

Conifer Removal
(All Phases)

Acres of Treated Area(s)

•

•

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Areas with intact sagebrush and understory vegetation present,
shrubs and herbs are the dominant vegetation that influences
ecological processes on the site.
Areas where trees are co-dominant with shrubs and herbs and
all three vegetation layers influence ecological processes on the
site.
Areas where trees are the dominant vegetation and the primary
plant layer influencing ecological processes on the site.
Selectively conducted to improve connectivity.

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Fuels Management

Area Closure
(Area and/or
Seasonal)
RESTORATION:
Post-Disturbance
and/or Habitat
Enhancement

Vegetation
Management /
Habitat
Enhancement

Acres of Fuels Treated

•

Includes projects that are designed to change vegetation
composition and/or structure to modify fire behavior
characteristics for the purpose of aiding in fire suppression and
reducing fire extent.

•

Conifer removals, which can be considered a fuels treatment,
are categorized separately and entered under Conifer Removal
(given that not every treatment objective related to conifer cuts
are fuels-management driven). However, the process of
downed trees and/or slash would be included in this subactivity.
May overlap spatial footprint associated with conifer removals.

•

Acres of areas closed permanently or seasonally in an attempt
to prohibit activities or land uses that may contribute to
sagebrush habitat loss or degradation.

•

Acres of projects or treatments aimed at improving existing,
intact sagebrush habitats. While many actions are covered
specifically, this subactivity allows to capture actions aimed at
improving sagebrush habitat as well as actions aimed at
improving others aspects of healthy sagebrush ecosystem
including but not limited to augmenting canopy coverage,
understory species diversity, and managing other shrubs that
may contribute to sagebrush habitat loss or degradation.
Includes projects that are designed to change vegetation
composition and/or structure by reducing the presence of
invasives annual grasses and/or forbs. Examples of this action
would be efforts to remove or reduce cheatgrass or
medusahead rye, among other species that degrade understory
health.

Acres

Acres of Treated Area(s)

•
Annual Grass Forb or
Noxious Weed
Treatments

Acres of Treated Area(s)

Energy development
reclamation with the
goal of sagebrush
restoration

Acres of Reclaimed Area(s)

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Table2. List of non-spatial project activities, subactivities, and metrics.
ACTIVITY

SUBACTIVITY

SAGEBRUSH
PROTECTION:

Conservation
Agreements
(including but not
limited to: CCAs,
CCAAs, Farm Bill and
other Incentivebased programs)
Conservation
Easements
Preventing
Subdivision

EXAMPLES AND INFORMATION TO INCLUDE (Objectives, Notes,
Effectiveness Narrative Boxes)

PROJECT METRICS
•

Acres Enrolled
•
•

Long-term or permanent easements put into place with the
specific objective of preventing urban development resulting in
sagebrush habitat loss, fragmentation, or degradation. Please
be sure to redact any PII from the information provided.

•

Provide the total number, and type of structures that were
removed or moved out of sagebrush habitats. Structures
typically include (but may not be limited to): communication
towers, cellular towers, abandoned windmills, abandoned
buildings, power lines (transmission or distribution), and wind
turbines.

•

Miles of power lines (transmission and distribution) buried to
reduce impacts to sagebrush dependent species

•

Miles of power lines (transmission and distribution) modified to
reduce impacts to sagebrush dependent species

•

Report miles of fence modified (i.e., smooth top wire) in areas
with high potential for sage-grouse strikes/collisions
documented. Consider including multiple fence marking
projects occurring within an area (i.e., population, watershed,
county, conservation district) together as opposed to entering
multiple records.

Acres Enrolled

Type of structure removed
Structure Removal
Amount Removed
RESTORATION:
Infrastructure
Removal and
Modification

Powerline Burial
Powerline
Retrofitting /
Modification

Fence Modification

Type of powerline
Miles of powerline buried
Type of Modification
Miles of powerline modified

Miles Modified

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Examples include Voluntary Federal, State, NGO, Local and
Tribal habitat restoration programs, Programmatic CCAs,
Programmatic CCAAs, Programmatic Restoration Plans for
Invasive Plants, and Programmatic Reclamation Plans. Include
the conservation effort implemented as part of the agreement
as well as reporting on effectiveness monitoring.
Please be sure to redact any PII from the information
provided.

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Fence Marking

Fence Removal

RESTORATION:
Livestock &
Rangeland
Management

Improved Grazing
Practices (Rest,
Rotation, Etc.)

•

Report miles of fence marked in areas with high potential for
sage-grouse strikes/collisions documented. Consider including
multiple fence marking projects occurring within an area (i.e.,
population, watershed, county, conservation district) together
as opposed to entering multiple records.

•

Report miles of fence removed in areas with high potential for
sage-grouse strikes/collisions documented. Consider including
multiple fence removal projects occurring within an area (i.e.,
population, watershed, county, conservation district) together
as opposed to entering multiple records.

•

Enter total acres of rangeland/ranchland being managed
according to NRCS Sage-Grouse Initiative grazing practices and
range management recommendations OR State or Federal
agency recommendations including:
o Rotating livestock to different pastures, while resting others
to establish a diversity of habitat types.
o Changing seasons of use within pastures to ensure all plants
have the ability to reproduce.
o Leaving residual cover (grass from the past season) to
increase hiding and nesting cover for sage-grouse.
o Managing the frequency and intensity of grazing to sustain
native grasses, wildflowers, and shrubs.
o Managing livestock access to water to ensure healthy
livestock and healthy

Miles Marked

Miles Removed

Acre (Associated w/
Allotments/Pastures in Practice)

o
RESTORATION:
Travel Management
SPECIES
MANAGEMENT:
Population
Augmentation

Road and Trail
closure

Miles

Rerouted Roads
and/or Trails

Miles

Translocation

Number of Sage-grouse
Translocated

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Targeted grazing aimed at reducing fine fuel loads

•

Miles of road removed, de-commissioned, or rerouted as well as
roads/trails that are closed for a defined period of time (while
remaining on the landscape) to reduce human activity in an
area.

•

Include the number of sage-grouse included in translocation
effort. Include information about where sage-grouse were
moved from, as well as where they are being moved to. Include
post-release effectiveness monitoring protocols.

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RESTORATION:
Feral Equid
Management

Feral Equid
Population Control

Number Feral Equids Treated

Feral Equid Gather

Number Feral Equids
Gathered/Removed

CED User Manual 2.0.0 Please check https://conservationefforts.org for updates

•

Number of free-roaming equids treated with population control
methods in order to achieve properly functioning condition for
riparian areas and/or rangeland health standards for sagebrush
communities.

•

Number of free-roaming equids gathered for relocation in order
to achieve properly functioning condition for riparian areas
and/or rangeland health standards for sagebrush communities.

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3.0 HOW WILL DATA IN THE CED BE USED?
The CED was designed to collect information on conservation efforts in an organized and spatially
explicit fashion so that we could better understand the full extent to which conservation actions are
ameliorating threats to the sagebrush ecosystem. The specifics of how we will quantitatively or
qualitatively assess the extent to which threats are ameliorated are currently in development. We are
working closely with modeling experts and structured decision making experts to develop a process that
fully accounts for the actions in the CED in a transparent and objective manner, and in a way that
appropriately accounts for uncertainty. There is potential for the CED to help identify geographic gaps
(or concentrations) in conservation efforts to help prioritize future conservation actions. As the CED
Team works with our partners to refine how data will be used, Appendix B will be updated to reflect
those discussions and describe paths forward.

4.0 REPORTING
The CED has undergone some significant updates from CED v1.0, as it relates to reporting
features/functionality. While the CED will retain the functionality to perform queries and generate
tabular summaries of the information, you, the user, have provided (or been given access to by the
providing party), the CED will now be able to generate a summary of information queried, along with a
map illustrating the efforts included, and some simple summary calculations.
While the CED’s mission and organization is focused on the sagebrush ecosystem, the CED will calculate
zonal statistics based on sage-grouse areas of interest and resource values (in the form of a population
index (Doherty et al. 2016) and breeding habitat distribution (Doherty et al. 2016). Additionally, the CED
will calculate the different amount of other resource information such as the resistance and resilience
(Chambers et al. 2016, 2017).
When generating a report, there is a lag between record entry and when the data is ‘available’ for
display, query, and map calculation. Please keep this in mind if you need a report. The CED Team will
work with partners and data providers to keep the CED updated on an annual basis list those dates on
reports generated.

5.0 PROJECT SITING
At a broad or regional scale, the CED can be used as a tool to view a variety of conservation efforts
aimed at sagebrush habitat improvement and/or threat reduction. By using the CED’s Interactive Map,
any user can view spatial data entered into the CED as well as query a smaller subset of actions or by
geographic area. This will allow the user to strategically site conservation efforts based on proximity to
other implemented actions. This approach has the potential to foster a community of collaborative
conservation.
Additionally, the CED has added new information in the form of spatial layers that can be displayed in
the background of our Interactive Map. This information can provide important context to geographic
areas based on resource values, sage-grouse values, and some threats. Some of these layers will also be
used to quantify conservation benefit and/or threat reduction as mentioned above in Section 5.0
(Reporting Features).
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6.0 INTEROPERABILITY
Various partners either currently have or are developing decision support tools and databases to collect
information and provide a mechanism for viewing, analyzing, or downloading that information. It is the
goal of the CED to work collaboratively with our partners to increase interoperability between the CED
and their respective tools. With that understanding, we hope to reduce the need for duplicate data
entry, while still ensuring the collection of all relevant information needed for long term monitoring and
evaluations of effectiveness.
The CED will not be able to provide every function needed by our partners. However, the CED can
connect with other tools to provide a more complete picture of the landscape, as well as help point
users to the tool(s) that best meet their needs. This will be a valuable feature of the CED.
As a part of implementation of the Integrated Rangeland Fire Management Strategy, an interagency
team led by the BLM and USGS has created a geospatial data catalog and enhanced data sharing tools
on the BLM Landscape Approach Data Portal. This effort provides many of the layers displayed in the
CED. The data portal provides access to data layers, map viewers, and analytical tools to support the
Strategy. The geospatial data catalog is a curated list of datasets and includes information from BLM,
USGS, FWS, and other partners.
Also connected to the Integrated Rangeland Fire Management Strategy, is the development of a
Conservation and Restoration (C&R) Strategy. A tool is being developed to provide access to information
in the C&R and help inform future proposed management actions at the landscape or regional scales.
The tool will tie into the CED to display various suites of conservation information. Additionally, the
USGS and BLM are building a complementary tool that will help with prioritizing and siting restoration
and habitat improvement projects at the site scale based on a host of characteristics including the
success of other treatments with similar characteristics. The CED Team is working with the development
of that tool to look for mutually beneficial opportunities.
The CED team has also worked closely to share information with our state partners to query data from
their existing databases including but not limited to the Oregon Watershed Enhancement Board, Utah’s
Watershed Restoration Initiative, and Wyoming Game and Fish’s databases which tracks a host of
information not limited to conservation actions.

7.0 ENTERING DATA IN THE CED
This section of the User’s Manual is designed to help new and returning CED users register for the
website and enter data. Additional resources can be found within the CED Help link
(https://conservationefforts.org/sgce/help/) and include help videos, batch upload instructions, and
table structure and documentation. Additionally, we have created a separate tab for Frequently Asked
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Questions (FAQs), and will continue to update this, as well as include the information in this
documents and/or the CED User Guide as appropriate. If you have questions or comments that cannot
be answered via the help resources please do not hesitate to contact us.
To reduce confusion, we have included the following definitions here, to guide users through the data
upload process. These terms, and others, are included in the Glossary located in Appendix A.
Data terms are defined as follows in the CED:
•

•

Metadata = the who, what, when, where, and how behind the data. Metadata for individual
efforts is captured as the plans are being entered. For example, who=project contact,
when=effort start and finish dates, etc. Metadata will need to be provided during batch
uploads of tabular or geospatial data in order to comply with Federal Geographic Data
Committee guidelines.
Attribute data = the information requested in the CED for a conservation plan or project (e.g.
activity, sub-activity, threat the effort is intended to help ameliorate, effectiveness information,
etc.). For individual efforts, the attribute data is required information to enter the plan or
project. When batch uploading tabular or geospatial data, some attribute data may be missing
and will need to be provided.

7.1 Individual Plan and Projects
Recognizing the limited resources and working relationships our conservation partners have, we
encourage the following prioritization approaches for entering conservation efforts in the CED:
•
•

•

Large and/or significant efforts that are most relevant to addressing threats to sagebrush within
the partners’ realm of influence are the highest priority efforts to enter in the CED.
If partners worked together to develop or implement an on-the-ground project, we suggest that
all involved partners create a set of ‘business rules’ to organize who is reporting the efforts to
reduce double counting. There is no one-size-fits-all approach given the varying levels of
coordination in each state, however partners are encouraged to work together to determine the
most efficient approach for entering projects that were implemented through partnership
efforts.
o For example, perhaps the partner that provided the majority of the funds or who led the
on-the-ground effort serve as the lead and enter the project information into the CED, if
practical.
Consider the merits of consolidating multiple small treatments involving similar activities into
one larger project for data entry purposes. This applies to actions in which the CED will not ask
for spatially-explicit information. For example, if multiple fence marking efforts have occurred
in one targeted area and have the same implementation and effectiveness information, the
registered CED user could combine those individual fence marking actions into one project entry
for the CED. This would save time and effort by creating one record/entry that describes the
total of the fence marking projects, rather than creating multiple individual lines with repetitive
project information for each fence that was marked.

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7.2 Batch Uploads
Many conservation partners will find it more efficient to batch upload information from their existing
databases rather than entering data for individual projects. The CED Team will be available to assist
with the batch uploading process. The first step will be to contact the CED Team Lead, identified in the
‘About CED’ page. Users will
download a file geodatabase
Partner
File
template and append their data to
Completion
CED
Database
Geodatabase
of Batch Data
the template. Once loaded in the
Fields
Template
CED, the database will add these
skeleton projects to the CED. Users
Figure 5. Batch upload flow diagram
will then be able to quickly complete
remaining data fields using batch entry within the CED website. This is a deviation from the previous
batch upload process and is intended to help reduce errors related to the previous batch upload
process. This process (Fig. 5) is still being developed and is subject to change at any time.

7.3 Geospatial Data
CED documentation and spatial data are housed on the Landscape Conservation Management and
Analysis Portal (LC Map), which is built upon ScienceBase, a collaborative scientific data and information
management platform. LC Map is managed by the Great Northern Landscape Conservation Cooperative
(GNLCC).
Geospatial data can be uploaded directly into ScienceBase as indicated in Appendix A (located under the
Help page of the CED). The organizational information provided by agencies and organizations for the
CED user registration process will also be used to organize ScienceBase folders for agencies and
organizations to post their geospatial data in ScienceBase.

7.4 Getting Started
In order to enter data into the CED, agencies/organizations must first provide information on their
agency/organization and office structure for the CED pre-registration process. This step is necessary
to ensure the security of the site and of each record entered into the CED. This pre-registration
process is used to complete the following security functions:
•
•

•

•

Development of the drop down menus for the user profiles
Identification of one or more “approving officials” or “gatekeepers” to ensure that
data providers entering information on behalf of the agency/organization are actually
from the agency/organization.
Designation of one or more “approving officials” to review and approve project and plan
records for public viewing and use by the Service. This step allows for quality control for
agencies/organizations.
Determining who has permission to modify conservation efforts for the agency/organization:
o the data provider that created the project,
o select employees within the data provider’s office, or

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o

the approving official for that project/plan.

To get started, please visit the Help page at https://conservationefforts.org and follow the instructions
for submitting this information. However, if your agency/organization already provided this
information in CED v1.0, it will be carried over. If you need to update contacts, and/or approving
officials, please follow the procedure described above.
7.4.1 Welcome Page
The CED Team has installed a new Welcome Page which directs users to the various CED features. This
is a hub allowing users to login (or logout), enter data (after logging in), explore information about
updates and outreach (such as fact sheets and webinars), and access the new Interactive Map directly.
Data entry options, along with the query function, will not be accessible to the user until after logging in.
Additionally, we have 2 new features in which state-specific modules can be accessed, and the ‘Decision
Support Tool and Data Catalog Library’ – where users can access an ever growing list of decision support
tools developed by Federal agencies as well as our partners. Each tool/catalog listed provides a brief
description of what the tool is, how to access it, along with contact information for each. If you see a
tool that you would like added to the library, simply contact the CED Team, and we will work with you to
get it added.

Figure 6. Welcome Page for CED v2.0.0.

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7.5 Register for an Account

Once the agency/organization has provided information on organizational structure and approving
officials, individual data providers will be able to register for an account. To register for an account, go to
https://conservationefforts.org/sgce/accounts/register/, or select the “REGSITER for the CED” button
(Fig. 6), which should bring you to the following page (Fig 7.):

Figure 7. Example registration page.

Proceed by entering your information, and click ‘Submit Registration’ (Fig. 7). You will receive an email
within several minutes, containing a link that will allow you to activate your account. Once your
account has been activated, proceed to the next step to enter your profile information.

7.6 Enter Profile Information
When you log in for the first time, you will automatically be directed to the ‘Main Page’ where you
will be asked to provide your contact information (see screenshot below). Fill out all required fields
marked with an asterisk (*). Approving officials should have already been designated for your
agency/organization, and will appear in a drop-down menu once your agency/organization or office is
selected. If you don’t see an approving official, please contact your agency lead for the CED. If you
don’t know who that is, contact the CED team fw1sagegrouseced@fws.gov for assistance. In addition,
if you do not see your office within the drop down list you can select DEMONSTRATION USER ACCESS
ONLY. Lief Wiechman will automatically be given as your approving official. Records entered in this
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test capacity can be converted from test records to real records when your profile information is
updated. Please contact the CED Team for further assistance with this step.
All data providers must accept the Terms of the agreement in order to be able to enter your
conservation efforts into the CED. Click ‘Email Approving Official’ to request access from your
approving official to enter data for your agency/organization. You cannot enter data until your
agency/organization’s approving official has authorized you to do so. You will receive an autogenerated email when that has occurred.

Figure 8. Example profile page.

** IMPORTANT NOTE FOR REGISTERED USERS: From this point forward in this
document, many hyperlinks will NOT take you to the desired page unless you
are logged-in to the CED. Please login to the CED to gain access to all of the
document’s assistance features. Additionally, you may want to set your default
browser to Google Chrome to ensure full functionality. **

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7.7 Create a New Project/Plan
You must be logged in to enter data (go to: https://conservationefforts.org/sgce/). After logging in,
select the ‘ENTER DATA’ button on the Welcome Page (Fig. 6) or from your user drop-down menu
(red arrow; Fig. 9). To enter a new conservation effort (project or plan) select ‘Create New Project.’
See Entering a Conservation Effort for further instructions.

Figure 9. Example data entry page.

7.8 Entering a Conservation Effort

In this section, we will guide you creating a record/entry for each of the 3 types of information being
collected in CED v2.0.0, ‘Plans’, ‘Non-Spatial Projects’, and ‘Spatial Projects’. Many of the steps will be
similar for each entry type; however the plans and non-spatial projects will not contain the spatial data
upload steps.

7.8.1 SPATIAL PROJECTS
Step 1: Conservation Effort Name & Completion Status
Indicate the name of the conservation effort (in this case, the name of the project) using fewer than
50 characters. Effort (plan or project) names cannot be duplicated within the CED. Useful tips for a
unique name include an effort name (often a geographical landmark), implementing agency, the
type of effort, and the year the effort began (Example: Idaho-BLM-Soda Fire Restoration-2016).
While we understand many users will agency-specific naming conventions, we prefer to avoid
strictly numeric names for each record.
Select an Effort Type, Activity, and Subactivity (in that order). Choosing these fields will cause
display the appropriate metrics and potentially other fields that need to be completed based on
your Subactivity selection. The ‘Implementing Party’ and ‘Office’ fields will be autopopulated
based on the individual’s profile that is entering the record. The ‘Date created’ field will be
autopopulated as well.
Not all projects will require spatially-explicit data. For a complete list of which projects will require
spatially-explicit data, refer to Table 1.

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Figure 10. Example record entry page.

Select an Implementation Status. Those efforts that are “In Progress” have been only partially
implemented and have not been completed. A conservation effort that would be considered
“Completed” no longer requires further actions aside from post-treatment monitoring
(effectiveness monitoring), or maintenance. The Implementing Party, Office, and Date
created fields are automatically filled using information from your user profile. While users
can edit these fields if necessary, we recommend using the default settings.
A unique conservation effort Project ID number will be assigned for each record (plan or project)
entered in the CED and is viewable in the leftmost column on the “User’s CED HOME” page (you
must be logged in to view) in the list of “My projects”. You will see above the ‘Save and Continue’
button, a notice that will state “You are creating a Spatial Project. Spatial data is required”.
Click ‘Save and Continue’ to proceed to the next page. This will advance you to the ScienceBase
footprint editor.

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#2
#3
#1

Figure 11. Footprint editor.

Footprint Editor – Spatial Data Upload and Digitizing
The CED will then redirect you to the USGS’s ScienceBase’s Footprinter (Fig. 11). This the step in
which a user can either upload existing spatial information in the form a shapefile, or use this tool to
hand-digitize the project’s boundary. Keep in mind, hand-digitizing may result in inaccuracies in GIS
calculations that will have to be addressed in a later step.
To upload existing shapefiles, select the “Select Zipped ShapeFile” button (red arrow #1; Fig. 11).
This will open a file browser where you can search and select which file to load. To hand digitize,
select one of the tools along the left side of the map (red arrow #2; Fig. 11). If using the digitizing
tool, a user can zoom in, to more accurately digitize. Furthermore, after a polygon is complete, a
few open (Delete, Zoom to Extent, Add Information) will appear below the “Save to Item” button.
Explore the functionality of each of these features to best represent the project polygon. The CED
will no longer collect line information, and in most cases will not collect point-data. Regardless of
the option you select, when the appropriate file has been loaded or the digitizing is complete, select
“Save to Item” in the upper right hand corner (red arrow #3; Fig. 11). Select “Yes, save” to save and
upload the spatial files you have digitized or uploaded to proceed. If at any point, you’d like to
return to the CED, you can select the cancel button. You will have an opportunity to edit spatial
data prior to submitting your information.

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Figure 12. Example footprint editor confirmation page.

After you save, you will have the option to return to the footprinter to edit or add new features or
return back to CED record entry. When you return to the CED, you will be brought to Step 2. Later,
in Step 4, you will notice that the CED has calculated the acreage associated with the spatial file(s)
provided. The CED will also provide a warning when GIS-calculated acreages are different from the
“Acres Treated” which is provided by the user. You can see an example of that warning message
below. In this case the user entered 350 acres, while the GIS-calculated acreage totaled 386.2.
Step 2: Location Information
A small map illustrating the spatial data uploaded (or digitized) will appear at the top of this page
(Fig. 12). The Western Association of Fish and Wildlife Agencies (WAFWA) Zones, Sage-grouse
Populations, States, Counties, and Hydrologic Unit Code (HUC) 12 Zone fields will be automatically
populated based on the spatial information entered prior to Step 2. The process applied to
automatically select the boxes in each of these fields uses GIS layers from our database.

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Figure 13. Example record map page.

To reduce the processing time, only the parts of these zones that intersect with the extent of the
sagebrush biome are included in our layers. If your spatial polygon’s perimeter falls outside of
sagebrush distribution, it is possible that some spatial data (e.g., a state) might be included while
others (e.g., HUC 12) are missed. Please verify that all of the correct locations are checked. If some
location information remains unchecked, please ensure that the spatial data you have entered is in
the correct location. If the spatial data you have entered is not in error, please email the CED team
at fw1sagegrouseced@fws.gov as you will not be able to pass the error check without all location
information fields completed.
This is the step in which you will select any collaborating partners who were involved in the
effort. This is a way to include all collaborating parties within a single effort while reducing
duplicate reporting. This does require effective communication and coordination with your
partners to reduce the risk of double reporting.
The ‘Ownership’ checklist will NOT be automatically populated (Fig. 14). Select the appropriate
land owners that correspond with your conservation area.

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Figure 14. Land ownership options.

To proceed to Step 3, click on “Go to Step 3”.
Step 3: Implementation and Effectiveness Information
The implementation status selected earlier will carryover and automatically populate Question 1
of Part 1 (Fig. 15). Please verify that it is correct before continuing. If an error was made, the
user can correct the implementation status in Part 1, Question 1. Fill in your response to the
Question 2. If your conservation effort was considered effective, you will need to explain why in
Question 2.

Figure 15. Example implementation and effectiveness page.

Please read through the questions in Part 2 and select the appropriate response for your
conservation effort. Part 2 is required if the effort implementation status is “In-Progress” (Fig.
16). Part 2 is required if the effort is highly likely to be effective, but has not been in place long
enough to determine, or if the effort is unlikely to be considered effective in Part 1.

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Figure 16. Example implementation and effectiveness page.

Step 4: Activity Information
Complete all of the available fields. You will have the option to provide any ‘notes’ you would
like to at this stage (Fig. 17), but please keep in mind this is not the only opportunity to provide
supplemental information associated with your plane entry; we’ll address that in this step.

Figure 17. Example activity information page.

Documentation
This is your opportunity to upload supporting documentation. Supporting documents are
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required to provide context and/or validation for the conservation effort (plan or project),
specifically identifying the monitoring protocols and any information describing how a project is
being or was implemented. Documents such as progress reports published/peer-reviewed
journal articles, effectiveness monitoring reports, and other written products can be useful to
better explain the project’s objective(s), or scope of the conservation project or plan, or explain
how any decision or regulation are demonstrating or have demonstrated related effectiveness.
Select files you wish to upload by clicking the ‘Choose Files’ button (Fig. 18).

Figure 18. Uploading documents (1/3).

A window will pop open that will allow you to navigate to your supporting documents. Please wait
for your files to upload and do not click the back or forward buttons. Multiple files can be
uploaded by using the 'Crtl' and 'Shift' commands. Once you have selected your files, click ‘Open’
to close the window. After you have selected your files to be uploaded, the “Upload” button
should appear (red arrow; Fig. 18). Select the Upload button (a small box will appear while your
file(s) load).

Figure 19. Uploading documents (2/3).

After the file(s) load, select a file type for each (red arrow #1; Fig. 20), and provide a brief
description of the document (red arrow #2; Fig. 20). To download the uploaded document(s)
during review or when an approving official is approving, select the “Download” button (red arrow
#3; Fig. 20).

CED User Manual 2.0 Please check https://conservationefforts.org for updates

Page 35

#1

#2

#3

Figure 20. Uploading documents (3/3).

Select the “Go To Review” button (upper right corner). This will advance you to the last page for
review of the entry prior to officially submitting for evaluation (and related features, such as
summarizing information in a query or report, and the ability to view the record on the map).
You may select any threats that your project addresses in this step. Please keep in mind, that
each threat selected will create a narrative box below. Those boxes must be populated with the
appropriate information or you will not be allowed to advance. This is an imperative step as the
information provided here (as well as in Step 3) will be used for evaluation of effectiveness,
should the information be assessed for any purpose (such as a future greater sage-grouse status
review, for example).

Figure 21. Example effectiveness information.

To proceed to Step 5, click on “Go to Step 5” (see arrow #1; Fig. 22). If you would like to stop (or
pause) entering information for this record, click on “Save and Exit” (see arrow #2; Fig. 22) and
your progress will be saved. You will be able to return to this step by logging in and ‘View My
Projects’ under the User’s CED HOME tab at the top of the screen. You may at any time review
your data to ensure that all of the required fields have been properly completed by clicking the
‘Review Entry’ button near the top (right) of the screen (see arrow #3; Fig. 22).

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#3

#2

#1

Figure 22. Record review, save, exit options.

IMPORTANT NOTE: To navigate the Edit Project page, you may click any of the buttons across the
top of the page to quickly go from one step to another. Any changes you make to the steps as you
navigate back and forth will be automatically saved, but ONLY TEMPORARILY. You must click ‘Save
and Exit’ before leaving the site to save the information you have entered (arrow #2; Fig. 22).
Closing your browser window or using the ‘Back’ button on your browser without first clicking
‘Save and Exit’ will result in loss of entered data. The site will warn you of any attempt to leave
the data entry page without first saving so that you can return to the page without losing any
data.
Step 5: Review and Submit Your Conservation Effort
Review the information you provided. Please note that fields with an asterisk are required and if left
unpopulated, the CED will not allow the record to be submitted.

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Figure 23. Example record review.
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This provides an opportunity to scroll and review all of the information provided as well as quickly
jumping to any step, by selecting the corresponding buttons (Fig. 23). In the upper right corner,
there is a red box highlighting the options to proceed, as well as some reminder statements that
have been in every step. Please use the “Back to Step ‘X’ ” button, rather than your browsers
back/forward button to navigate the steps in the record. You can “Save and Exit” at any step if there
is an issue. If the page freezes or a button does not appear, please contact us immediately so we
may find and repair that bug. Select the “Save and Submit for Approval” button when the review is
complete. The CED will then send the Approving Official identified in the User’s Profile, notifying
them there is a record (plan or project) that is ready for their review and submission to be added to
the database. Again, this will allow for those records to be illustrated on the interactive map, be
subject to query/filter, and some activities will be calculated against risk and resources layers for
reporting purposes.
7.8.2 NON-SPATIAL PROJECTS
Step 1: Conservation Effort Name & Completion Status
Indicate the name of the conservation effort (in this case, the name of the project) using fewer than
50 characters. Effort (plan or project) names cannot be duplicated within the CED. Useful tips for a
unique name include an effort name (often a geographical landmark), implementing agency, the
type of effort, and the year the effort began (Example: Idaho-BLM-Soda Fire Restoration-2016).
While we understand many users will agency-specific naming conventions, we prefer to avoid
strictly numeric names for each record.
Select an Effort Type, Activity, and Subactivity (in that order). Choosing these fields will cause
display the appropriate metrics and potentially other fields that need to be completed based on
your Subactivity selection. The ‘Implementing Party’ and ‘Office’ fields will be autopopulated
based on the individual’s profile that is entering the record. The ‘Date created’ field will be
autopopulated as well.
Not all projects will require spatially-explicit data. For a complete list of which projects will not
require spatially-explicit data, refer to Table 2.

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Figure 24. Example record entry page.

Select an implementation status for the effort. “Planned” status is for conservation efforts
have not been implemented in any way. Those efforts that are “In Progress” have been only
partially implemented and have not been completed. A conservation effort that would be
considered “Completed” no longer requires further actions aside from post-treatment
monitoring (effectiveness monitoring), or maintenance. Projects may fall into any category,
however if the project is not completed, please ensure information is provided as to why the
project will (if planned) or is trending towards being effective.
If you do not see a subactivity that accurately represents the project you are attempting to
enter, please contact the CED Team at fw1sagegrouseced@fws.gov, and we will work with
you to find or create the appropriate space for your effort.
A unique conservation effort Project ID number will be assigned for each record (plan or project)
entered in the CED and is viewable in the leftmost column on the “User’s CED HOME” page (you
must be logged in to view) in the list of “My projects”. You will see above the ‘Save and Continue’
button, a notice that will state “You are creating a Non-Spatial Project. You can only load spatial
data as .pdf maps in documentation”. As a reminder, the CED will not be collection spatial data for
all records as it has done in the past.
Click ‘Save and Continue’ to proceed to the next page, which should look similar to Figure 25.
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Figure 25. Example non-spatial activity information page.

Step 2: Location Information
For records/entries that require spatially-explicit information, the CED will use that information to
autopopulate the location information. Because the CED will not be collecting spatially-explicit
information for plans, the user will select the associated geographic units for summarization
purposes.

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Figure 26. Example location information page.

Select each state and county where the treatment is located. If known, select all of the
corresponding land ownership where the project covers or will cover. This is also your opportunity
to identify any collaborators for the effort. Collaborators can be from a funding or implementation
stand point. We encourage users to include this information in the project summaries uploaded in
Step 4. You will see a red box in the screenshot above highlighting the “Go to Step 3” button. This
will advance you to Step 3, where answers are provided to questions related to implementation
and effectiveness of the effort.
Step 3: Implementation and Effectiveness Information
The implementation status selected earlier will carryover and automatically populate Question 1
of Part 1 (Fig. 27). Please verify that it is correct before continuing. If an error was made, the
user can correct the implementation status in Part 1, Question 1. Fill in your response to the
Question 2. If your conservation effort was considered effective, you will need to explain why in
Question 2.

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Figure 27. Example implementation and effectiveness page.

Please read through the questions in Part 2 and select the appropriate response for your
conservation effort. Part 2 is required if the effort implementation status is not “Completed”.
Part 2 is required if the effort is highly likely to be effective, but has not been in place long
enough to determine, or if the effort is unlikely to be considered effective in Part 1.

Figure 28. Example implementation and effectiveness page.

To proceed to Step 4, click on “Go to Step 4”.
Step 4: Activity Information
Complete all of the available fields. You will have the option to provide any ‘notes’ you would
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like to at this stage, but please keep in mind this is not the only opportunity to provide
supplemental information associated with your plane entry; we’ll address that in this step.
You may select any threats that your project addresses in Step 4. Please keep in mind, that each
threat selected will create a narrative box below. Those boxes must be populated with the
appropriate information or you will not be allowed to advance. This is an imperative step as the
information provided here will be used for evaluation of effectiveness, should the information be
assessed for any purpose (such as the 2020 greater sage-grouse status review, for example).
IMPORTANT NOTE: To navigate the Edit Project page, you may click any of the buttons across the
top of the page to quickly go from one step to another. Any changes you make to the steps as you
navigate back and forth will be automatically saved, but ONLY TEMPORARILY. You must click ‘Save
and Exit’ before leaving the site to save the information you have entered (see screenshot
below). Closing your browser window or using the ‘Back’ button on your browser without first
clicking ‘Save and Exit’ will result in loss of entered data. The site will warn you of any attempt to
leave the data entry page without first saving so that you can return to the page without losing
any data.
Documentation
This is your opportunity to upload supporting documentation. Supporting documents are
required to provide context and/or validation for the conservation effort (plan or project),
specifically identifying the monitoring protocols and any information describing how a project is
being or was implemented. Documents such as progress reports published/peer-reviewed
journal articles, effectiveness monitoring reports, and other written products can be useful to
better explain the project’s objective(s), or scope of the conservation project or plan, or explain
how any decision or regulation are demonstrating or have demonstrated related effectiveness.
Select files you wish to upload by clicking the ‘Choose Files’ button (Fig. 29).

Figure 29. Uploading documents (1/3).

A window will pop open that will allow you to navigate to your supporting documents. Please wait
for your files to upload and do not click the back or forward buttons. Multiple files can be
uploaded by using the 'Crtl' and 'Shift' commands. Once you have selected your files, click ‘Open’
to close the window. After you have selected your files to be uploaded, the “Upload” button
should appear (Fig. 30). Select the Upload button (a small box will appear while your file(s) load).
CED User Manual 2.0 Please check https://conservationefforts.org for updates

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Figure 30. Uploading documents (2/3).

After the file(s) load, select a file type for each (red arrow #1; Fig 31), and provide a brief
description of the document (red arrow #2; Fig 31). To download the uploaded document(s)
during review or when an approving official is approving, select the “Download” button (red arrow
#3; Fig 31).

#1

#2

#3

Figure 31. Uploading documents (3/3).

Select the “Go To Review” button (upper right corner). This will advance you to the last page for
review of the entry prior to officially submitting for evaluation (and related features, such as
summarizing information in a query or report, and the ability to view the record on the map).
Step 5: Review and Submit Your Conservation Effort
Review the information you provided. Please note that fields with an asterisk are required and if left
unpopulated, the CED will not allow the record to be submitted.

CED User Manual 2.0 Please check https://conservationefforts.org for updates

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Figure 32. Example record review.

This provides an opportunity to scroll and review all of the information provided as well as quickly
jumping to any step, but selecting the corresponding buttons. In the upper right corner, there is a
red box highlighting the options to proceed, as well as some reminder statements that have been in
every step. Please use the “Back to Step 4” button (Fig. 32), rather than your browsers
back/forward button to navigate the steps in the record. You can “Save and Exit” at any step if there
is an issue (Fig. 32). If the page freezes or a button does not appear, please contact us immediately
so we may find and repair that bug. Select the “Save and Submit for Approval” button when the
review is complete. The CED will then send the Approving Official identified in the User’s Profile,
notifying them there is a record (plan or project) that is ready for their review and submission to be
CED User Manual 2.0 Please check https://conservationefforts.org for updates

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added to the database. Again, this will allow for those records to be illustrated on the interactive
map, be subject to query/filter, and some activities will be calculated against risk and resources
layers for reporting purposes.
7.8.3 PLANS
Step 1: Conservation Effort Name & Completion Status
Indicate the name of the conservation effort (in this case, the name of the plan) using fewer than 50
characters. Plan names cannot be duplicated within the CED. Useful tips for a unique name include
an effort name (often a geographical landmark), implementing agency, the type of effort, and the
year the effort began (Example: Idaho-BLM-Soda Fire Restoration-2016). While we understand
many users will agency-specific naming conventions, we prefer to avoid strictly numeric names for
each record.
Select an Effort Type, Activity, and Subactivity (in that order). Choosing these fields will cause
display the appropriate metrics and potentially other fields that need to be completed based on
your Subactivity selection. The ‘Implementing Party’ and ‘Office’ fields will be autopopulated
based on the individual’s profile that is entering the record. The ‘Date created’ field will be
autopopulated as well.

Figure 33. Figure 10. Example record entry page.

Select an Implementation Status. Those efforts that are “In Progress” have been only partially
implemented and have not been completed. A conservation plan that would be considered
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“Completed” would be fully implemented. Through that rationale, most ‘plans’ will have a
status of “In Progress” until they have been fully implemented.
You can select either of the activities relating to ‘plans’ to peruse the available subactivities
nested within each activity. If you do not see a subactivity that accurately represents the plan
you are attempting to enter, please contact the CED Team at fw1sagegrouseced@fws.gov,
and we will work with you to find or create the appropriate space for your effort.
A unique conservation effort Project ID number will be assigned for each record (plan or project)
entered in the CED and is viewable in the leftmost column on the “User’s CED HOME” page (you
must be logged in to view) in the list of “My projects”. You will see above the ‘Save and Continue’
button, a notice that will state “You are creating a Non-Spatial Plan. You can only load spatial data
as pdf maps in documentation”. As a reminder, the CED will not be collection spatial data for all
records as it has done in the past. For ‘plans’ and a subset of the ‘projects’ the CED will obtain
relative location information by allowing the user to select from a pre-determined set of options.
Click ‘Save and Continue’ to proceed to the next page, which should look similar to Fig. 34.

Figure 34. Example location information page.

Step 2: Location Information
For records/entries that require spatially-explicit information, the CED will use that information to
autopopulate the location information. Because the CED will not be collecting spatially-explicit
CED User Manual 2.0 Please check https://conservationefforts.org for updates

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information for plans, the user will select the associated geographic units for summarization
purposes.
Select each state and county where the treatment is located. If known, select all of the
corresponding land ownership where the project covers or will cover. This is also your opportunity
to identify any collaborators for the effort. Collaborators can be from a funding or implementation
stand point. We encourage users to include this information in the project summaries uploaded in
Step 4. You will see a red box in the screenshot above highlighting the “Go to Step 3” button. This
will advance you to Step 3, where answers are provided to questions related to implementation
and effectiveness of the effort.
Step 3: Implementation and Effectiveness Information
The implementation status selected earlier will carryover and automatically populate Question 1
of Part 1 (Fig. 35). Please verify that it is correct before continuing. If an error was made, the
user can correct the implementation status in Part 1, Question 1. Fill in your response to the
Question 2. If your conservation effort was considered effective, you will need to explain why in
Question 2.

Figure 35. Example implementation and effectiveness page.

Please read through the questions in Part 2 and select the appropriate response for your
conservation effort. Part 2 is required if the effort implementation status is not “Completed”.
Part 2 is required if the effort is highly likely to be effective, but has not been in place long
enough to determine, or if the effort is unlikely to be considered effective in Part 1.

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Figure 36. Example implementation and effectiveness page.

To proceed to Step 4, click on “Go to Step 4”.
Step 4: Activity Information
Complete all of the available fields. You will have the option to provide any ‘notes’ you would
like to at this stage, but please keep in mind this is not the only opportunity to provide
supplemental information associated with your plane entry; we’ll address that in this step.
You may select any threats that your project addresses in Step 4. Please keep in mind, that each
threat selected will create a narrative box below. Those boxes must be populated with the
appropriate information or you will not be allowed to advance. This is an imperative step as the
information provided here will be used for evaluation of effectiveness, should the information be
assessed for any purpose (such as the 2020 greater sage-grouse status review, for example).
IMPORTANT NOTE: To navigate the Edit Project page, you may click any of the buttons across the
top of the page to quickly go from one step to another. Any changes you make to the steps as you
navigate back and forth will be automatically saved, but ONLY TEMPORARILY. You must click ‘Save
and Exit’ before leaving the site to save the information you have entered (see screenshot
below). Closing your browser window or using the ‘Back’ button on your browser without first
clicking ‘Save and Exit’ will result in loss of entered data. The site will warn you of any attempt to
leave the data entry page without first saving so that you can return to the page without losing
any data.

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IMPORTANT NOTE: To navigate the Edit Project page, you may click any of the buttons across the
top of the page to quickly go from one step to another. Any changes you make to the steps as you
navigate back and forth will be automatically saved, but ONLY TEMPORARILY. You must click ‘Save
and Exit’ before leaving the site to save the information you have entered (see screenshot
below). Closing your browser window or using the ‘Back’ button on your browser without first
clicking ‘Save and Exit’ will result in loss of entered data. The site will warn you of any attempt to
leave the data entry page without first saving so that you can return to the page without losing
any data.
Documentation
This is your opportunity to upload supporting documentation. Supporting documents are
required to provide context and/or validation for the conservation effort (plan), specifically
identifying the monitoring protocols and any information describing how a plan is being or was
implemented. Documents such as progress reports published/peer-reviewed journal articles,
effectiveness monitoring reports, and other written products can be useful to better explain the
plan’s objective(s), or scope of the conservation project or plan, or explain how any decision or
regulation are demonstrating or have demonstrated related effectiveness.
Select files you wish to upload by clicking the ‘Choose Files’ button (Fig. 37).

Figure 37. Uploading documents (1/3).

A window will pop open that will allow you to navigate to your supporting documents. Please wait
for your files to upload and do not click the back or forward buttons. Multiple files can be
uploaded by using the 'Crtl' and 'Shift' commands. Once you have selected your files, click ‘Open’
to close the window. After you have selected your files to be uploaded, the “Upload” button
should appear (Fig. 38). Select the Upload button (a small box will appear while your file(s) load).

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Figure 38. Uploading documents (2/3).

After the file(s) load, select a file type for each (red arrow #1; Fig. 39), and provide a brief
description of the document (red arrow #2; Fig. 39). To download the uploaded document(s)
during review or when an approving official is approving, select the “Download” button (red arrow
#3; Fig. 39).

#1
#2

#3

Figure 39. Figure 20. Uploading documents (3/3).

To proceed to Step 5, click on “Go to Step 5”.
Step 5: Review and Submit Your Conservation Effort
Review the information you provided. Please note that fields with an asterisk are required and if left
unpopulated, the CED will not allow the record to be submitted.

CED User Manual 2.0 Please check https://conservationefforts.org for updates

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Figure 40. Example record review.

This provides an opportunity to scroll and review all of the information provided as well as quickly
jumping to any step, but selecting the corresponding buttons (Fig. 40). In the upper right corner,
there is a red box highlighting the options to proceed, as well as some reminder statements that
have been in every step. Please use the “Back to Step 3” button, rather than your browsers
back/forward button to navigate the steps in the record. You can “Save and Exit” at any step if there
is an issue. If the page freezes or a button does not appear, please contact us immediately so we
may find and repair that bug. Select the “Save and Submit for Approval” button when the review is
complete. The CED will then send the Approving Official identified in the User’s Profile, notifying
CED User Manual 2.0 Please check https://conservationefforts.org for updates

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them there is a record (plan or project) that is ready for their review and submission to be added to
the database. Again, this will allow for those records to be illustrated on the interactive map, be
subject to query/filter, and some activities will be calculated against risk and resources layers for
reporting purposes.

8.0 NEXT STEPS
You will receive an email when your submitted project or plan has been successfully approved (by the
‘Approving Official’. When you return to the ‘View My Projects’ page
(https://conservationefforts.org/sgce/viewprojects/), you will notice that the ‘Entry Type’ code in the
last column will be “3” for your approved conservation project or plan. Once you see that ‘3’,
congratulations! You’ve successfully submitted a conservation effort to the Sage Grouse CED.
If your project or plan was not approved, you will need to communicate and coordinate with the
approving official in your respective agency/organization to make the necessary revisions, and
resubmit the project or plan for approval.

9.0 VIEW AND EDIT A PROJECT/PLAN
Visit the ‘View my Projects’ page at https://conservationefforts.org/sgce/viewprojects/ to select a
conservation effort for editing. Click the name to open the project or plan. When logged into the
CED, this menu option will be on the data entry menu.

10.0 DELETE A PROJECT/PLAN
While entering your project data, you will notice small red text near the top of the page that says
‘Mark this Effort for Deletion’ (Fig. 41). Check the box to next to the red text and click ‘Save and Exit.’
An email will be sent to your approving official. The approving official can select ‘Approve’ to submit a
CED effort to the CED administrators for final deletion.

Figure 41. Example for deleting a record

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11.0 BATCH UPLOAD
The CED has the ability to query from and upload existing datasets in bulk or batch format. While
more efficient than single record data entry there are still steps that need to be taken.
•
•

•

Contact the CED Team via email (fw1sagegrouseced@fws.gov) to request a batch upload.
Work with the CED Team/USGS to determine which fields from your datasets/databases
will need to be transferred to the CED. Once the fields have been determined, the USGS
will work with data providers and/or stewards to create crosswalks for the batch upload
process.
After the data has been uploaded, each project or plan will still need to be reviewed
by the data provider, to identify gaps in the transferred data.

Visit the Batch Upload page to learn more: https://conservationefforts.org/sgce/batch_upload/

12.0 INTERACTIVE MAP and REPORTING
One of the new features of the CED is our Interactive Map which allows users to view data related to
conservation efforts, but also resource information used in evaluation or for siting. Users can access the
Interactive Map from several places including the Menu Bar (red arrow #1; Fig. 42), the User’s drop
down (red arrow #2; Fig. 42), and the ‘INTERACTIVE MAP’ button on the welcome page (red arrow #3;
Fig. 42).

#1
#2

#3

Figure 42. Welcome Page for CED v2.0.0.
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The Interactive Map allows the user to complete simple queries based on a number of fields including
Activity Type, State, and more. The Interactive Map also has the ability to produce summarized reports
based on underlying spatial layers and resource values. Summary reports are generated from the spatial
data provided, meaning that spatial data needs to be accurate to prevent over estimates in the reports.
The CED Team is currently working with our partners to ensure data collection moving forward has
spatial data that is truly representative of the efforts, and do not contain significant portions of lands
not treated or included in the effort.
At this time, reports are not available for download, but we will be adding that feature in an upcoming
update, so that summary information may be used for reporting purposes. At this time, we ask users to
coordinate with the CED Team to ensure accuracy of the information used in the Interactive Map’s
summary reports. Additionally, there may be a time lag associated with when users provide data, when
they are ‘approved’ and submitted to the CED. Only after that point will the information be available for
reporting/query purposes. The CED Team wants to ensure users have a date stamp informing them of
when the data was provided last.

13.0 RECORD QUERY
This section is under development.

14.0 SUBMIT A BUG REPORT
The CED is a new website, and as such, errors and glitches are bound to crop up during its initial
implementation. Please help us by filling out a Bug Report whenever you find that something is
confusing or a page is not functioning properly. Bug Reports are easy to create, require just a minute
or two to complete, and are easily found under the Help tab. You may also click the link provided
here: https://docs.google.com/a/fws.gov/forms/d/1ugrfzbkNutUJda3LU2iyAYprvdlJe_Ug9UGSCjfT_4/viewform

15.0 ASK A QUESTION
Do you have a question about the CED or require assistance? Please use our form to submit a
question: https://docs.google.com/a/fws.gov/forms/d/1ugrfzbkNutUJda3LU2iyAYprvdlJe_Ug9UGSCjfT_4/viewform. If you require an immediate response, you can also send an email to
fw1sagegrouseced@fws.gov.

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APPENDIX A – Glossary
Attribute data: The information requested in the CED for a conservation plan or project (e.g. activity,
sub-activity, threat the effort is intended to help ameliorate, effectiveness information, etc.). For
individual efforts, the attribute data is required information to enter the plan or project. When batch
uploading tabular or geospatial data, some attribute data may be missing and will need to be provided.
Candidate Conservation Agreement (CCA): Voluntary conservation agreements between the US Fish &
Wildlife Service and one or more public or private parties to address the conservation needs of
proposed or candidate species, or species likely to become candidates, before they become listed as
endangered or threatened. The Service works with its partners to identify threats to the species, plan
the measures needed to address the threats and conserve these species, identify willing landowners,
develop agreements, and design and implement conservation measures and monitor their effectiveness.
Candidate Conservation Agreement with Assurances (CCAA): Voluntary conservation agreements that
provide non-federal landowners with additional incentives beyond a CCA for engaging in voluntary
proactive conservation through assurances that limit future conservation obligations. One of the
primary reasons for developing the CCAA program is to address landowner concerns about the potential
regulatory implications of having a listed species on their land. The CCAA program specifically targets
non-federal landowners and provides them with the assurance that if they implement various
conservation activities, they will not be subject to additional restrictions if the species becomes listed
under the ESA.
Conservation Easement: A legal agreement voluntarily entered into by a property owner and a qualified
conservation organization such as a land trust or government agency. The easement contains
permanent restrictions on the use or development of land in order to protect its conservation values.
Easement restrictions vary greatly for each agency or organization.
Endangered Species Act (ESA): Law which serves to protect and recover imperiled species and the
ecosystems upon which they depend. Under the ESA, species may be listed as either endangered or
threatened.
Equids: Free-roaming horses (Equus caballus) and burros (E. asinus).
Hydrologic Unit Code (HUC): A system of dividing and sub-dividing the United States into successively
smaller hydrologic units or drainage areas.
Implementation Status: The stage in which a particular efforts (or suite of efforts) are classified as at the
time when the information is submitted.
- In-Progress: A treatment that is still undergoing activity leading up to post-treatment
monitoring.
- Completed: No additional actions are needed at the site, the effort is considered ‘complete’
from an implementation stand point. Post-treatment monitoring (effectiveness monitoring)
is being conducted, should adaptive management actions be needed to achieve effort
objectives.

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Metadata: The who, what, when, where, and how behind the data. Metadata for individual efforts is
captured as the plans are being entered. For example, who=project contact, when=effort start and
finish dates, etc. Metadata will need to be provided during batch uploads of tabular or geospatial data
in order to comply with Federal Geographic Data Committee guidelines.
Lek: An aggregation of males that gather to engage in competitive displays to attract attending females
for mating.
Project: In a general sense, an action, treatment, or effort to implement conservation on the ground.
Not to be confused with the BLM’s use of the term “project” which is a collection of various treatments
conducted within a ‘project area’.
Range Improvement: Any activity, structure, or program on or relating to rangelands which are designed
to improve production of forage, change vegetative compositions, control patterns of use, provide
water, stabilize soil and water conditions, and provide habitat for livestock and wildlife. The term
includes, but is not limited to, structures, treatment projects, and use of mechanical means.
Reclamation: Rehabilitation of a disturbed area to make it acceptable for designated uses. This normally
involves re-contouring, replacement of topsoil, re-vegetation, and other work necessary to ensure
eventual restoration of the site.
Restoration: Implementation of a set of actions that promotes plant community diversity and structure
that allows plant communities to be more resilient to disturbance and invasive species over the longterm. The long-term goal is to create functional, high-quality habitat that is occupied by sage-grouse.
The short-term goal may be to restore the landform, soils, and hydrology, and increase the percentage
of preferred vegetation, seeding of desired species, or treatment of undesired species.
Western Association of Fish and Wildlife Agencies (WAFWA): Association which advocates for the rights
of 23 states and Canadian provinces to manage fish and wildlife within their borders. The WAFWA sagegrouse technical committee developed objectives in 1999 to maintain and increase where possible the
present distribution and abundance of sage-grouse.
Wildland Fire: Any non-structure fire that occurs in the vegetation and/or natural fuels. Includes both
prescribed fire and wildfire.

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APPENDIX B – Proposed Uses/Analyses for Data Collected
Agriculture Conversion / Tillage Risk:
To more precisely evaluate the potential risk to sage-grouse from future agricultural conversion, we will
replicate the analysis conducted for the 2015 greater sage-grouse status review. For a brief description
of the proposed analysis, please see information below.
(Excerpts from the 2015 Not-Warranted Finding) Rates of agricultural conversion likely slowed and will
continue to slow because the most productive sagebrush habitats have already been converted to
croplands or pasturelands (Baker et al. 1976). Since 1982, acres of new cropland within occupied sagegrouse range have decreased in every State except South Dakota (NRCS 2013), likely due to the
decreasing suitability of the remaining habitats for agriculture. However, economic incentives for
biofuels and technological advances in irrigation and cultivation could potentially increase conversion
rates in the future (Knick et al. 2011). In 2010, we determined that agricultural conversion would
continue to affect sage-grouse in the future based on historical loss and fragmentation of sage-grouse
habitat from agricultural conversion.
For the analysis, we compared a new cropland suitability model (Lipsey et al. 2015) with the Population
Index (Doherty et al. 2016). The cropland suitability model uses soil and climate data to predict the
probability that an area could be converted to cropland (Lipsey et al. 2015). The Population Index model
identifies important sage-grouse population centers (Doherty et al. 2016). By comparing these two
models, we quantified the percent of the Population Index that overlapped with sagebrush habitats in
the MZ I that have a high potential to be converted to agriculture in the future. Because the cropland
suitability model was only finalized for MZ I for reasons explained below, the results of this exercise
specifically apply only to MZ I, but can be used to assess potential probabilities of conversion to
agriculture rangewide.
The cropland suitability model was developed only for the Great Plains (MZ I), and not for the Columbia
Basin (MZ VI) or the Snake River Plain (MZ IV), where agricultural conversion also occurred, due to the
limited availability of land cover data, the small size of the Columbia Basin (MZ VI), and differences in the
way sage-grouse use agricultural fields between these three MZs. Additionally, more of the Columbia
Basin (MZ VI) has already been converted to cropland (Knick et al. 2011) and the Great Plains (MZ I) has
the highest percentage (69 percent) of private lands, so the potential risk of agricultural conversion is
greatest in the Great Plains (MZ I). As a result, the cropland suitability model focused only on the MZ
with the greatest potential to be converted in the future, so our overlay analysis with the sage-grouse
breeding distribution model could only be calculated in the Great Plains (MZ I).
We will utilize data collected in the CED, in the form of conservation easements (with the distinct
purpose of preventing tillage of sagebrush habitats), wildlife management areas, and land acquisitions
(acquired with the specific purpose of preventing tillage and managing for characteristics representative
of healthy sagebrush habitats, to evaluate their benefit to greater sage-grouse (or other obligate
species) by comparing against the Population Index model referenced above, as well as if the cropland
suitability model to assess the amount of potential threat that has been addressed given the probability
it contains the characteristics of suitable cropland.
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Oil and Gas Development:
To more precisely evaluate the potential risk to sage-grouse from oil and gas development, we will
replicate the analysis conducted for the 2015 greater sage-grouse status review. For a brief description
of the proposed analysis, please see information below.
(Excerpts from the 2015 Not-Warranted Finding) For this status review, we used peer-reviewed and
published methodologies (Copeland et al. 2009, entire) to model the probability of future oil and gas
development impacting sage-grouse. The model focused on assessing the risk of nonrenewable energy in
MZs I and II, the two areas with the highest potential for future nonrenewable energy development
(Juliusson and Doherty 2017). Although nonrenewable energy development potential exists and will
continue in the Uinta-Piceance Basin (MZ VII), the model not applied to MZ VII because the relative
proportion of potential development was low, even under the highest development scenario. The model
used geological information illustrating potentially available oil and gas resources to map areas of likely
future development (Juliusson and Doherty 2017). We also used Oil & Gas Resource Assessments
developed by the USGS to incorporate future maximum potential development scenarios into the
analysis (Juliusson and Doherty 2017). The analysis quantified potential effects to sage-grouse we
quantified the percent of the Population Index (Doherty et al. 2016) as well as the modeled Breeding
Habitat Distribution (Doherty et al. 2016) potentially exposed to future energy development based on the
availability of oil and gas resources.
We will utilize data collected in the CED, in the form of Federal Land Use Decisions, No Surface
Occupancy restrictions, and conservation easements (land include jurisdiction over subsurface mineral
rights, that prevent or limit the development in the easement area), as well as other regulatory
protections that can be illustrated spatially, to evaluate their benefit to greater sage-grouse (or other
obligate species) by comparing against the Population Index and Breeding Habitat Suitability models
referenced above, as well as if layers depicting development scenarios as described above.
Conifer Encroachment:
We are currently exploring ways to evaluate the conservation benefit from conifer removals efforts
including but not limited to responses described in Baruch-Mordo et al. (2013), as well as methods used
by partner agencies.
We are evaluating current products available to spatially illustrate where conifers are encroaching into
sagebrush ecosystems. Those products include a layer created by the BLM National Operating Center
for use in tracking disturbance as part of the BLM and USFS Monitoring Framework which could provide
valuable insight. Furthermore, mapping product described in Falkowski et al. (2017) can offer valuable
information as to where conifer is encroaching into sagebrush habitats and in relation to sage-grouse
habitats.
In 2017, the Rangeland Ecology & Management produced a special issue, including a series of
publications that describe the benefit achieved through conifer removals which provides insight into
how these actions can be effective at conservating sagebrush habitats that sage-grouse and other
sagebrush dependent species rely on.

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Invasives / Annual Grasses:
We are currently exploring ways to evaluate the conservation benefit from actions aimed at reducing or
eliminating invasive annual grasses (cheatgrass, medusa head, etc.). It is our hope to work with subject
matter experts to not only identify the spatial information that might best illustrate where infestations
occur, but also information to help evaluate[biological] effectiveness of the various efforts.
Wildfire:
We are currently exploring ways to evaluate and quantify the conservation benefit from actions aimed
at reducing the impacts of wildfire, notably habitat loss and subsequent incursion of invasives annual
grasses. We are also looking into ways to better quantify the conservation benefit of pre-suppression
actions such as fire breaks.
Sagebrush and Sagebrush Obligate Resource Values:
We are in the process of identifying spatial information in addition to those layers that illustrate
breeding habitat (Doherty et al. 2016) and relative population index (Doherty et al. 2016) for greater
sage-grouse to expand to other sagebrush dependent species. Work being conducted through the
WAFWA Sagebrush Conservation Strategy may provide information that could satisfy this need.
Additionally, we are including the Resistance and Resilience information (Chambers et al. 2014, 2016,
2017), and will continue to make improvements to calculate the amount of overlap between
conservation efforts and these layers.

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APPENDIX C – Literature Cited
Baker, M., R. Eng, J. Gashwiler, M. Schroeder, and C. Braun. 1976. Conservation Committee Report on Effects of
Alteration of Sagebrush Communities on the Associated Avifauna. The Wilson Bulletin, 88(1; 165-171).
Baruch-Mordo, S, J.S. Evans, J.P. Severson, D.E Naugle, J.D. Maestas, J.M. Kiesecker, M.J. Falkowski, C.A. Hagen,
K.P. Reese. 2013. Saving sage-grouse from the trees: a proactive solution to reducing a key threat to a
candidate species. Biological Conservation 167 (233–241).
Chambers, J.C., D.A. Pyke, J.M Maestas, M. Pellant, C.S. Boyd, S.B. Campbell, S.E. Espinosa, D.W. Havlina, K.E.
Mayer, A. Wuenschel. 2014. Using resistance and resilience concepts to reduce impacts of invasive annual
grasses and altered fire regimes on the sagebrush ecosystem and greater sage-grouse: A strategic multi-scale
approach. Gen. Tech. Rep. RMRS-GTR-326. Fort Collins, CO: U.S. Department of Agriculture, Forest Service,
Rocky Mountain Research Station. 73 p.
Chambers, J.C., J.L. Beck, S. Campbell, J. Carlson, T.J. Christiansen, K.J. Clause, J.B. Dinkins, K.E Doherty, K.A. Griffin,
D.W. Havlina, K.F Henke, J.D. Hennig, L.L Kurth, J.D. Maestas, M. Manning, K.E.Mayer, B.A. Mealor, C.
McCarthy, M.A. Perea, D.A. Pyke. 2016. Using resilience and resistance concepts to manage threats to
sagebrush ecosystems, Gunnison sage-grouse, and Greater sage-grouse in their eastern range: A strategic
multi-scale approach. Gen. Tech. Rep. RMRS-GTR-356. Fort Collins, CO: U.S. Department of Agriculture, Forest
Service, Rocky Mountain Research Station. 143 p.
Chambers, J.C.; Beck, J.L.; Bradford, J.B.; Bybee, J.; Campbell, S.; Carlson, J.; Christiansen, T.J.; Clause, K.J.; Collins,
G.; Crist, M.R.; Dinkins, J.B.; Doherty, K.E.; Edwards, F.; Espinosa, S.; Griffin, K.A.; Griffin, P.; Haas, J.R.; Hanser,
S.E.; Havlina, D.W.; Henke, K.F.; Hennig, J.D.; Joyce, L.A.; Kilkenny, F.M.; Kulpa, S.M.; Kurth, L.L.; Maestas, J.D.;
Manning, M.; Mayer, K.E.; Mealor, B.A.; McCarthy, C.; Pellant, M.; Perea, M.A.; Prentice, K.L.; Pyke, D.A.;
Wiechman, L.A.; Wuenschel, A. 2017. Science framework for conservation and restoration of the sagebrush
biome: Linking the Department of the Interior’s Integrated Rangeland Fire Management Strategy to long-term
strategic conservation actions. Part 1. Science basis and applications. Gen. Tech. Rep. RMRS-GTR-360. Fort
Collins, CO: U.S Department of Agriculture, Forest Service, Rocky Mountain Research Station. 213 p.
Copeland, H.E., K.E. Doherty, D.E. Naugle, A. Pocewicz, J.M. Kiesecker. 2009. Mapping Oil and Gas Development
Potential in the US Intermountain West and Estimating Impacts to Species. PLoS ONE 4(10): e7400.
doi:10.1371/journal.pone.0007400
Doherty, K. E., J. S. Evans, P. S. Coates, L. M. Juliusson, and B. C. Fedy. 2016. Importance of regional variation in
conservation planning: a rangewide example of the Greater Sage-Grouse. Ecosphere 7(10):e01462.
10.1002/ecs2.1462
Falkwoski, M.J., J.S. Evans, D.E. Naugle, C.A. Hagen, S.A. Carleton, J.D. Maestas, A.H. Khalyani, A.J. Poznanovic, A.J.
Lawrence. 2017. Mapping Tree Canopy Cover in Support of Proactive Prairie Grouse Conservation in Western
North America. Rangeland Ecology & Management 70(1; 15–24).
Juliusson, L. M., and K. E. Doherty. 2017. Oil and gas development exposure and conservation scenarios for Greater
sage-grouse: Combining spatially explicit modeling with GIS visualization provides critical information for
management decisions. Applied Geography 80:98-111.
Lipsey, M.K., K.E. Doherty, D.E. Naugle, S. Fields, J.S. Evans, S.K. Davis, N. Koper. 2015. One step ahead of the plow:
Using cropland conversion risk to guide Sprague's pipit conservation in the northern Great Plains. Biological
Conservation 191 (739–749).
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U.S. Fish and Wildlife Service. 2013. Greater Sage-grouse (Centrocercus urophasianus) Conservation Objectives:
Final Report. U.S. Fish and Wildlife Service, Denver, CO. February 2013.

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