Environmental Policy Solutions
Our mission is to help solve complex environmental problems using a holistic, collaborative approach.
Friday, September 9, 2016
Gabrielle Feldman's Breathe California interview!
I recently had the honor of being interviewed by Breathe California's executive director on my local cable channel. We discussed a wide range of topic including the new San Francisco Bay Restoration Act and the impacts of fire on our health! Please take a few minutest to check out my interview! http://www.creatvsj.org/207-2/?showid=27336&channel=1
Thursday, July 23, 2015
Consequences of Sustainability - Guest Post by Susan Schneider
As long term strategic planners, we are often asked to
take abstract concepts that require forecasting into the future and create
logical solutions that we can implement now in the hopes of creating a
sustainable solution for current problem. This can not only be a daunting task
but require decision makers to take out their crystal balls and predict the
future. In our world, the crystal ball is usually an extensive uncertainly
model, years of monitoring data, or maps generated with layers of data, but the
reality is that we use these tools to help us make predictions about the future
so that we can develop long terms plans now. This is essential and if done
correctly, can result in highly productive and sustainable solutions for a
diverse set of issues. Long term planning is a key feature of any sustainable
program and is the hallmark of sustainability. The following piece explores
this concept in more detail.
Today, I am excited to introduce Dr. Susan Schneider
as our guest blogger. She has packed a lot into a short piece where she looks
at the consequences of sustainability with regard to overfishing. Susan
Schneider, PhD is the author of the award-winning book The Science of
Consequences and has just completed a book tour of 90 talks across the US and
Scandinavia. Her book brings an
inclusive interdisciplinary approach to learning principles, their biological
context, and their many applications, including sustainability. The book received coverage in Nature. As a
Visiting Scholar at the University of the Pacific, Schneider holds graduate
degrees in engineering (Brown) and psychology (University of Kansas). She has been a board member for several Audubon
chapters for 14 years, and is currently seeking to transition from academia to
the nonprofit sector. You can email Susan Schneider at sschneider@pacific.edu
to learn more about her work.
Consequences
for Sustainability
Susan
M. Schneider
“Incentives are the cornerstone of modern life. And
understanding them—or, often, ferreting them out—is the key to solving just
about any riddle.” - Levitt & Dubner, Freakonomics
One of the poster children for sustainability riddles
is overfishing. The late 20th century
collapse of the Atlantic shad and cod fisheries are just two of the more recent
examples in a long history. As
award-winning journalist Tom Horton noted of the Chesapeake Bay’s depleted shad
fishery: "By 1890, bay watermen had
responded to the relative scarcity in the same, time-honored fashion they still
often follow - they redoubled harvesting efforts and developed more efficient
catching methods" (Bay Country, p. 45). It’s a matter of short-term vs long-term consequences. Guess which ones often win.
Individually, too:
Even when long-term consequences are as sure as anything can be - such
as painful tooth decay and expensive dental work - people can still put off
dentist visits. Throw in a little
uncertainty and toss the wiser choice with it.
A riddle indeed.
Native Americans kept their harvesting of Atlantic
shad sustainable. It was only with the
arrival of the European colonists that overfishing became a problem. Early regulations were largely ignored, and
in 1738 a full-scale battle ensued.
Lives were lost.
We can project
benefits-to-costs ratios over time, and Cambridge Professor Andrew Balmford did
just that for a number of environmental policy challenges like overfishing (Science). Going for the desirable long-term
consequences of sustainability often brought very high ratios - but in the face
of substantial short-term costs. Can we
develop strategies to help surmount this barrier?
Yes, but we need all the help we can get. Nobel Prize-winning environmental economist
Elinor Ostrom wrote of the “complex, multivariable, nonlinear, cross‑scale, and
changing systems" that made careful tailoring essential for success in
addressing each challenge. With a
multitude of factors to consider, an interdisciplinary analysis is often
essential. But it can be helpful to
remember that everything still comes down to lots of individual choices -
choices influenced by their consequences.
One of the relevant sciences has long focused on the
role of consequences. In The Science
of Consequences, I cover the principles of learning from consequences,
their biological context, and their wide range of applications. Researchers in this area worked out the
mathematics of the most typical drop in consequence value over time: the "delay discounting" function
that is pivotal in behavioral economics as well. Not surprisingly, the longer the delay, the
more the consequences get discounted.
That’s just the beginning of analyses based on the functions of our
choices, and all the factors influencing them.
A few of the many success stories:
* US Safe Harbor programs provide incentives for
landowners to preserve habitat for endangered species. Andrew Balmford again (Wild Hope): Despite
Endangered Species Act protection, a woodpecker species was losing ground. When the arrival of these birds meant
increased liability and restrictions, landowners used techniques like
preemptive logging to avoid these consequences. Instead, putting out the welcome mat under a
Safe Harbor agreements offered protection, and sometimes cost-sharing. So far, most landowners have been happy.
* Utilities send community comparison reports to
consumers, with happy faces for reduced energy use. It made a difference in places like
California, Minnesota, and Washington. Once
new habits become established – turning off lights, unplugging
"vampire" electronics - how much easier to maintain a more
sustainable lifestyle.
* In a very direct approach, arid Las Vegas
successfully paid residents to switch from water-wasting lawns to water-wise
yards. Again, once established, people adapt
to the new lifestyle (as they've done with recycling). And there's much to appreciate in addition to
the savings in water charges: more birds
and butterflies and (often) decreased maintenance. New social norms have developed, helping to support
the new look and change attitudes.
These are all positive strategies that make
economic sense as well. Positive
consequences aren’t just what we hope for when we work toward
sustainability. They’re an essential
tool to help us get there.
References
Atlantic States Marine Fisheries Commission.
"Shad and River Herring," website, consulted July 13, 2015. http://www.asmfc.org/species/shad‑river‑herring
Balmford, A. Wild Hope: On the Front Lines of
Conservation Success. Chicago:
University of Chicago, 2012.
Balmford, A., A. Bruner, P. Cooper, R. Costanza, S.
Farber, R. E. Green, M. Jenkins, et al. “Economic Reasons for Conserving Wild
Nature.” Science 297 (2002): 950–53.
Horton, T. Bay
Country. Baltimore, MD: Johns
Hopkins, 1987.
Levitt, S. D., & S. J. Dubner. Freakonomics: A
Rogue Economist Explores the Hidden Side of Everything. New York: Morrow,
2005.
Ostrom, E. “A Diagnostic Approach for Going beyond
Panaceas.” Proceedings of the National Academy of Sciences 104 (2007):
15181–87.
Schneider, S. M.
The Science of Consequences: How They Affect Genes, Change the Brain,
and Impact Our World. Amherst, NY:
Prometheus, 2012.
Schneider, S. M.
"For Presidents' Day (US): Sustainability, Consequences, and the
‘Founding Fish.’" Web blog post,
The Science of Consequences, February 22, 2013.
Tuesday, April 21, 2015
Conducting Research for Strategic Plans that follow an Integrated Approach to Natural Resource Management
Strategies for Conducting Research Using an Integrated Approach to
Natural Resource Management
Many of the environmental challenges we face are
so complex that it almost seems impossible to identify the heart of the
problem, let alone identify and prioritize solutions, trade-offs, and potential
conflicts for the given problem. My advice is to always start by taking a step
back to attempt to see the 25,000 foot view before diving into the specific
problems. This type of approach enables you to identify all of the parts of the
problem before you start to understand each part individually and then together as
an entire system. This is often referred to as a systems approach with the goal
of ensuring that every perspective is considered and addressed throughout the
planning process. Another important aspect at this stage in the planning
process is to attempt to remain as open as possible to all of the information
you come across and evaluate each piece of information on its own merits. This
will allow you to remain as unbiased as possible during the information
gathering stage of the planning process.
At this stage of the game, you need to
understand what the issues are, who the stakeholders are, and what the
overlapping and competing issues that contribute to the issue at hand are.
Before you meet with a stakeholder group or attempt to identify and prioritize
the issues, it is pertinent to conduct a detailed assessment of the history of the
problem, identify the historical conflicts between stakeholders, understand past
planning efforts, and identify trends for the future. The following case
study is an assessment of the combined impacts of climate change and invasive
species on island ecosystems. It provided the necessary background information
needed to develop an integrated strategic plan that was later used to develop
projects for biodiversity conservation, as well as identify potential impacts
to island ecosystems from the combined effects of climate change and invasive
species.
This case study is a summary of the expected
impacts from climate change on islands, from invasive species on islands, and
their likely combined effects. Additionally, the assessment reviews the social,
political, and economic effects of both climate change and invasive species on island
biodiversity. This information was used to help inform the stakeholder
working group, set priorities that were rooted in science, and educate the
stakeholders so that they were contributing to the strategic plan in an
effective manner. Moreover, this type of inclusive assessment allowed us to
ensure that each stakeholders concerns and needs were taken into consideration
during the strategic planning process.
As usual, I welcome your comments or questions. Thank you, Gabrielle
Outlining the Combined
Effects of Climate Change and Invasive Species on Islands
Expected Impacts from Climate Change
to Marine Life and Small Islands
·
Many important coastal habitats that provide
benefits to human society and the environment alike are also highly likely to
experience severe declines.
·
Higher sea level and warmer ocean temperatures
can alter ocean circulation and current flow, increase the frequency and intensity
of storms, alter habitat, and impact weather worldwide (Baker et al. 2008,
Carpenter et al. 2008, Bakun 1990, Nicholls et al. 1999, and Bindoff et al.
2007).
·
Despite the differences in erosion potential
along the world’s coastlines, there has been a dramatic increase in coastal
erosion over the last two decades (Morton et al. 2004) and this is expected to
continue as sea level rises (Brown and McLachlan 2002) and storm frequency and
severity increase.
·
Rising sea level is most threatening to low
lying island nations and the delta populations of South and Southeastern Asia
and the Nile Delta in Africa (Nicholls et al. 2007 and Nicholls et al. 1999).
·
Many climate change impacts are likely to affect
island communities in both the Caribbean and Pacific, including higher sea
levels, more powerful tropical storms (such as hurricanes in the Atlantic and
typhoons in the Pacific), and warmer, more acidic coastal waters. Unique island
ecosystems, such as coral reefs and mangrove forests, are already facing stress
from human development and pollution, making them particularly sensitive to additional
stresses from climate chance (USGCRP 2009).
·
Islands are home to unique ecosystems and
species that provide economic opportunities, safety, nourishment, and cultural
value to island communities (USGCRP 2009 and Mimura et al. 2007).
·
The loss and inundation of other coastal
habitats, such as mangroves, from sea level rise and storm surge could endanger
species that use these habitats for nesting, nursing, and nutrients (USGCRP
2009).
·
Climate change may enhance conditions that facilitate
the spread of invasive species and marine and terrestrial pathogens and
diseases, which would affect and island’s natural ecosystem and biodiversity
(Mimura et al. 2007).
Impacts from Invasive Species on
Island Ecosystems
·
The Earth has approximately 100,000 islands many
of which are important biodiversity hotspots made up of fragile ecosystems that
are home to some of the most unique species in the world (CBD 2010). Island
ecosystems are key areas for biodiversity conservation worldwide since they
represent less than 5% of the planet’s land mass, yet are home to 39% of
critically endangered species (Whittaker 1998, Diamond 1985, 1989, Olson 1989).
Island species are more susceptible to environmental stressors that cause
extinctions as a result of their small population sizes and limited habitat
availability. In addition, island species have adapted in isolated environments
making them particularly vulnerable to impacts from invasive species (Diamond
1985, 1989, Olson 1989).
·
It is widely accepted that the natural world is
facing a very high rate of species extinction (Raup 1988), that most recent
extinctions can be directly attributed to human activity (Diamond 1989), and
that for ethical, cultural, aesthetic, and economic reasons this current rate
of extinction is cause for considerable concern (Ehrlich 1988, Ledec and
Goodland 1988). One of the major worldwide causes of anthropogenic extinctions
is the introduction of invasive species. Of the 245 recorded animal species
extinctions since 1500, 75% were species endemic to islands (World Conservation
Monitoring Centre 1992). Invasive species were at least partially responsible
for a minimum of 54% of documented island extinctions, based on the 170 island
species for which the cause of extinction is known (Ricketts et al. 2005).
·
The effects of invasive species on islands
accounts for 80% of all species extinctions recorded so far. Half of these
recorded extinctions were caused by invasive alien vertebrates (IAV) such as
rats, mice, pigs, goats, etc. Rodents (rats and mice), the most prolific of all
invasive vertebrates, are estimated to have been introduced to more than 80% of
the world’s islands as the result of human activities. Invasive species
continue to invade new islands today with the ever-increasing movement of
people and goods around the world. When introduced to islands, invasive species
upset an island’s natural equilibrium and severely impact native plants and
animals that lack adaptations to protect themselves from the intruders. There
is a relatively simple, efficient, and cost effective solution to this
island-species extinction crisis: when invasive species are removed from
islands, native plants, animals, and ecosystems recover with little or no
additional intervention. Combined with effective biosecurity, the eradication
of invasive species is one of the most effective ways to protect threatened
island biodiversity.
How do Invasive Species aggravate the
effects of Climate Change on biodiversity?
·
Climate change and invasive species are
considered by many scientists to be the greatest threats to biodiversity by the
21st Century. Climate change is projected to negatively impact
global GDP by as much as 20%, while invasive species are expected to impact the
GDP by as much as 5% of the global economy in the coming years. The combined
effect of climate change and invasive species is estimated to be around 25% of
the global economy by 2050 with the greatest impacts expected to occur on small
islands (Burgiel and Muir 2010).
·
The effects of invasive species are expected to
be exacerbated with a changing climate by creating conditions that favor
species that are highly adaptable and resilient to change, like invasive
species (UNEP 2006). For example, Hellman et al. 2008 found that extreme
weather events, shifting currents, and altered circulation patterns could
enhance invasive species ability to disperse to new areas where they will
likely have an advantage in overcoming biotic constraints and outcompeting
native species. Researchers in New Zealand are concerned that invasive mammals
like black rats, which are key drivers of the extinction rates of native
species, are highly likely to adversely impact biodiversity conservation and
ecosystem function with the combined effects of climate change (Tompkins et al.
2013). The Australian Invasive Species Council has identified five likely
combined effects of climate change and invasive species to the native biota in
Australia including the following (Invasive Species Council 2009):
1.
Range changes due to new temperature and
precipitation patterns
§
Hill et al. 2013 has determined that climate
change is decreasing the productivity of Antarctic krill by decreasing the
overall concentration of chlorophyll-a. Antarctic krill accounts for
approximately 85% of Antarctic fur seal, 76% of grey-headed albatross, and 12%
of wandering albatross diets. Any degradation of Antarctic krill growth habitat
is likely to have consequences on predators on South Georgia Island, which
could cause serious declines in their population.
2.
Increased opportunity for invasive species
incursion into new areas during extreme or abrupt weather events
§
Cook et al. 2010 has linked the glacial retreat
on South Georgia Island with the increased incursion rate of rats into
previously unoccupied areas of the island as a direct result of glacial retreat.
This risk has serious implications for the important breeding populations of
ground nesting seabirds on the island.
3.
Increased susceptibility of native species to
invasive species
§
A USGS 2006 report has determined that native
Hawaiian birds are being decimated by avian malaria and pox transmitted by
introduced mosquitoes. Invasive feral pigs exacerbate the problem by providing
habitat for mosquito larvae by feeding on tree fern trunks. It has been
determined that by reducing artificial larval habitat and removing feral pigs
the mosquito population will be effectively reduced, which is the best hope for
limiting disease transmission.
4.
Increased chance of biosecurity breach with
human responses to climate change
§
There are few if any documented cases of
incursion as a result of conservation or restoration efforts; however, humans
are the primary cause of the spread of invasive species. Witmer et al. 2011,
summarized some of the reasons why human caused incursion are likely to occur:
·
People often cannot distinguish between native
and invasive species
·
People are unaware of how their quality of life,
economy, biodiversity, and conservation can be significantly affected by
invasive species
·
Many people believe in the sanctity of all life
whether invasive or not and do not want invasives removed
·
Many people have an inherent dislike or distrust
of the use of chemicals and toxicants even though they may be necessary tools
for invasive species management
5.
Increases in carbon emissions by removing native
vegetation that sequesters carbon
§
Godson 2008 assessed the risk that invasive
rabbits have on vegetation in Australia and evaluated their potential to
decrease carbon sequestration. Research found that 2 rabbits per hectare can
decrease plant regeneration by 75%. Furthermore, there are concerns that an
increasing rabbit population will create a high risk of rabbits consuming
seedlings that were planted for carbon sequestration.
·
Climate change is also likely to shift predator
prey behavior through habitat modification, rising sea temperatures, ocean
acidification, shifting marine and terrestrial community structures, and
altered migratory patterns. These projected changes can lead to prey switching
potentially increasing the threat to native species from both climate change
and invasive species.
1.
Iverson et al. 2014 recorded drops in prey
fitness under changing predatory pressures. In particular, they found that
polar bears were increasing predation pressure on Arctic seabirds with the loss
of suitable marine mammal prey.
2.
These types of shifting patterns that are likely
to affect all migratory and marine species will be exacerbated by the negative
effects of invasive species. Furthermore, it is predicted that the multiple and
varied effects of climate change will affect every pillar of biodiversity and
that sensitive species, that are often found on islands, are likely to exceed
their ecosystem thresholds or “tipping point” potentially resulting in
extinction (Rinawati et al. 2013). Species that have reached a tipping point
can respond in three ways: change, move, or die.
·
In order to minimize the likely outcome of many
island dependent species from reaching their ecological tipping point, an
integrated holistic approach to conservation and management of climate change
and invasive species is essential to increase the resilience and adaptability
of native species (Burgiel and Muir 2010). The Global Invasive Species
Programme identified three key messages that are fundamental in integrating invasive
species and climate change impacts across multiple sectors and regions. The key
messages include (Burgiel and Muir 2010):
1.
Climate change will have direct and indirect
impacts that will facilitate the introduction and spread of invasive species,
2.
Invasive species will likely increase the vulnerability
of ecosystems to adapt to other climate related stressors, as well as reduce
their carbon sequestration potential, and
3.
Using an adaptive ecosystem based approach, the
above pressures can be offset by preventing the introduction of new invasive species
and by eradicating and controlling the invasive species that are already
present.
·
Eradicating invasive species from islands will
have tremendous benefits for native species that are combating the combined
effects of invasive pressures with a changing climate. Stress is one of the
leading causes of species extinction and by eradicating invasive species from
islands, multiple stressors will be relieved simultaneously. Invasive species eradications
have a twofold benefit to impacted species by decreasing the direct and
indirect effects of invasive predators and increasing overall resilience of
biodiversity in the face of a changing climate.
Monday, March 16, 2015
Developing a Comprehensive Community Engagement Plan
Developing a
Comprehensive Community Engagement Plan is a fundamental component of any successfully
environmental program and can provide great insight into any social or
political barriers to implementation, as well as help identify key
stakeholders, and tease out potential points of controversy and potential trade-offs.
Typically the goal of any community
engagement plan is to gain public and agency buy-in for a project, as well as
identify potential problems that could derail the project or result in
litigation.
A successful
outreach campaign should include the following key components a) clearly
defined driving forces, goals, and objectives; b) holistic understanding of the
target audience including the demographics, attitudes and behaviors, barriers
to action, and a strategy to package and distribute your message (e.g. websites,
FAQ’s, talking points, etc.); and c) metrics to track the success of the
outreach campaign, as well as a plan to adaptively management the outreach
strategy for the duration of the outreach phase of the project.
The goal of
a successful outreach campaign should be transparency and public buy-in. For
these reasons, you must identify all of the relevant stakeholders and actively
conduct outreach to them. In the following Case Study we targeted groups that
were clearly opposed to the proposed project, in addition to those that were
supportive of the project and willing to write letters of support or more.
There are several reasons that I advocate for the direct engagement with
opposition groups: First, it is a gesture to the group acknowledging their
interest and potential influence over the outcome of the project. Second, it
allows you the opportunity to understand the group’s issues, reservations, and
potential areas of compromise during the planning process. And finally, direct
engagement and compromise are the best methods to reduce the likelihood of
litigation or injunction against the project.
As a case
study, I have provided an example of the Community Engagement Plan that was
cooperatively developed with the US Fish and Wildlife Service and partner NGO’s
for the proposed mouse eradication project on the Farallon Islands. I was a key
member of the core partnership and the lead author of the Draft Environmental
Impact Statement, as well as the project director for outreach and
communications for select NGO partners. In the outline below, I have identified
the key aspects of an effective strategic outreach plan with specific examples
based from the Farallon Islands project. Please feel free to ask questions or
provide feedback. Thank you,
Gabrielle
Case Study: Farallon Islands Proposed Mouse
Eradication Draft EIS Outreach Campaign
The Key
Components of an Outreach Campaign Include:
A. Defining driving forces, goals, and
objective
a.
The primary driving force behind the
proposed mouse eradication was to remove invasive house mice from the Farallon
Islands to restore the ecosystems on the islands and protect native species
including ashy storm-petrels, endemic arboreal salamanders, endemic cave
crickets, and other species.
i.
The specific needs for this outreach campaign
were to educate the public on the need for mouse removal, to clearly explain
the differences between the use of rodenticides on the mainland for rodent
control purposes and the use of rodenticides designed for conservation purposes
on islands, and to gain support for the project.
b.
The goals of the project include:
i.
Conduct outreach with interested parties and
gain support from permitting agencies, NGOs and individuals prior to the
release of the DEIS, as well as during the public comment period
ii.
Educate the public and interested parties about
the project and the Farallon Islands
iii.
Hold a public meeting that was well attended and
prevented grandstanding
iv.
Work with the media to ensure that the project
is projected in a good light
c.
The objects of the project include:
i.
Gather signatures for a letter of support for
the project prior to the release of the DEIS
ii.
Conduct an embargoed press release to ensure
positive press coverage of the project on the release of the DEIS and the
announcement in the Federal Register
iii.
Develop a website, FAQs, fact-sheets, talking
points, press releases, and more for the project
iv.
Give radio interviews that are well informed,
provided insight to the project, and ensured that it is viewed in a good light
B. Identify the target audience including the
demographics, attitudes and behaviors, and barriers to action
a.
The target audience for the outreach
associated with the Farallones project included:
i.
Animal Rights groups that oppose all of the
potential alternatives proposed
ii.
Anti-pesticide groups that oppose all of the
potential alternatives proposed
iii.
Environmental Interest Groups that understand
the need for action, approve of the proposed alternatives, and support the
project
iv.
General public that is uninformed about the
project and need for action, as well as a need to provide information that will
give them a better understanding of the project, understand the need to act,
and the rationale behind the proposed alternatives
v.
Agencies that will be providing and approving
permits, if the project is implemented
b.
The primary barriers to action include:
i.
Animal Rights groups and anti-pesticide groups
could seek an injunction claiming that the FWS did not sufficiently evaluate
all of the potential alternatives available to remove mice from the islands.
1.
To overcome this barrier we actively
communicated with detractor groups, invited them to participate in public
meetings, and comment on the DEIS. We
kept them in the loop with regard to outreach to interested parties. We also
controlled their ability to grandstand during the public meeting and in the
media through the design of the public meeting and outreach protocol.
ii.
Agency buy in to the project that will need to
issue and approve permits
1.
To overcome this barrier we met with every
agency that has a stake in the permitting of this project, gave presentations
to their staff, and allowed them to comment on the project and identify the
path forward to receiving a permit through their agency
iii.
Public trust is an issue because many citizens
do not trust the FWS to act in the best interest of the public with regard to
the management of public lands
1.
To overcome this barrier we worked with the
public to answer any questions they had and allowed the public to feel like
their input was going to be considered prior to choosing a preferred
alternative. For this reason, the FWS and its partners did not choose a
preferred alternative for the DEIS to allow the public to weigh in on the
decision.
iv.
Activist groups mistrust the motivation of some
of the partner NGOs and claiming that they advocate for pesticides for
pesticide companies
1.
To overcome this barrier the NGO in question took
a backseat during the public meeting to show that the FWS owns the project and
that the NGO’s interests lie in the restoration and conservation of the island
rather than the method used to remove the mice.
It was also made clear that this NGO’s role in this project was only in
the compliance and outreach processes and not the implementation. Additionally,
I crafted a policy statement on the NGO’s position on the use of conservation
rodenticides, as well as submitted comments to Cal DPR in support of its
proposal to restrict the use of second generation anticoagulants in California.
c.
Messaging - Creating, packaging, and
distributing a message
i.
The FWS and its partner NGOs worked together for
several years to determine the ideal messaging for this project. We created several factsheets, FAQs, blog
posts, and talking points that presented the project in the best light
possible. Additionally, all of the partners were relaying the same message to
the public, agencies, and interested parties.
ii.
The partners framed the message in a way that
would ensure that our message in support of the project was clear, transparent,
and owned up to the risks rather than attempting to bury them.
iii.
We used several different media and outreach
approaches to ensure that the project was branded properly and steered clear of
potential conflicts through social media.
C. Evaluating the campaign
a.
Metrics used to Track campaign success
i.
The campaign directly before and during the
public comment period was highly successful at achieving it’s intended goals:
1.
The partnership received support from over 20
NGO groups and individuals on the sign on letter
2.
We held over 5 different radio interview that
were highly successful Over 20 articles, blogs, and interviews were written and
the majority of them portrayed the project in a positive light.
3.
We received buy in and support from all
permitting agencies and approval of much of the DEIS and the planning
processes.
b.
Adaptive Management Plan used as a
framework adaptive decision making during the campaign
i.
We developed a framework for decision making
that included a command structure, risk scenarios, tipping points, contingency
plans, and adaptive protocols
1.
We developed potential risk scenarios based on
perceived or known concerns with stakeholder groups, agencies, or other
influential group
2.
Based on what we knew about the different
stakeholder, we held regular meeting to discuss outreach to those parties and
determine if our protocol had changed or if a tipping point in the campaign had
been reached that would negative affect our preferred outcome.
3.
Risk scenarios were developed and modified
throughout the implementation of the outreach campaign based on media, social
media, agency, or public responses to the DEIS and public meeting. A tipping
point, or threshold, was developed for each risk scenario, and a contingency
plan was developed for each risk scenario.
4.
A chain of command was developed for decision
making and adaptive management in order to ensure that decision were made in an
orderly and logical manor.
Friday, February 20, 2015
Strategies for Streamlining Compliance for Restoration Projects: Case Study - Streamlining Compliance for Rodent Eradication Projects in the United States
Outlining Strategies to Streamlining Compliance for Restoration Projects
One of the biggest complaints that I hear on a regular basis has to do with the gridlock and seemingly endless bureaucracy involved in planning a restoration project. I often hear that the cost of planning makes the project infeasible. So the question is, how can we effectively comply with environmental regulations while simultaneously implementing restoration projects without long delays? The answer is to streamline the compliance process.
What do I mean by streamlining compliance? Streamlining the compliance process is ideal for restoration projects that are likely to be implemented in multiple locations over multiple years. A good example might be shoreline restoration to prepare for sea level rise. This is something that needs to be done anywhere there is a shoreline, making it an ideal candidate. An analyst, could then identify all of the necessary permits and regulatory processes, including environmental impact assessment, and work with regulatory agencies to develop programmatic permitting processes or other similar approaches that will cut down on the planning time. Other ways to streamline compliance include developing templates and standard language that can be easily used for multiple projects. Additionally, modelers could develop tools that would allow analysts to easily evaluate impacts or design mitigation strategies.
To illustrate how one might go about developing a program to streamline compliance, I am sharing a paper that I wrote on this subject for rodent eradication projects in the United States. I presented my work at the 2014 Vertebrate Pest Conference in Hawaii, and the following article was published in the Conference Proceedings. The approach outlined in this paper is similar to one that I would take for any issue. It is first imperative to have a holistic understanding of the problem, an updated understanding of the regulatory aspects of project planning, and the role that social and political issues will play in the implementation of the project. Please feel free to ask any question or provide feedback in the comments. Thank you,
Gabrielle
From Planning to Implementation: Streamlining
Compliance for U.S. Rodent Eradications
By: Gabrielle
Feldman and Gregg Howald
Abstract
Implementing
rodent eradication projects on federally owned islands in the U.S. can take ten
or more years to plan and often accounts for more than 50% of total project
expenses. Consequently, identifying ways to improve planning efficiency by
streamlining the compliance process will allow land managers to restore more
islands thereby increasing ecosystem productivity, and improve species resilience.
The compliance process, defined here as fulfilling National Environmental
Policy Act (NEPA) requirements and securing all necessary state and federal permits,
creates a valuable and robust framework to examine goals, develop alternatives,
assess anticipated impacts, establish partnerships, and engage the public, as
well as provides permitting agencies and the public an opportunity to
participate in the planning process. One significant challenge to the planning
process is that many variables that need to be accounted for early in the
process are social, economic, or political in nature and are frequently
overlooked, downplayed, or disregarded. We reviewed the planning documents for
several rodent eradication projects and identified areas where the process
could be streamlined, described lessons learned, and made recommendations for
future projects. Streamlining can be achieved
by identifying programmatic solutions, understanding social and political
constraints, and developing a robust, transparent assessment of a range of
alternatives.
Key
Words: environmental
compliance, environmental planning, invasive species, NEPA, rodent eradication,
streamlining compliance, stakeholder relations.
Introduction
Invasive
Species on Islands
The
Earth has approximately 100,000 islands many of which are important
biodiversity hotspots made up of fragile ecosystems that are home to some of
the most unique species in the world (CBD 2010). Island ecosystems are key
areas for biodiversity conservation worldwide since they represent less than 5%
of the planet’s land mass, yet are home to 39% of critically endangered species
(Whittaker 1998, Diamond 1985, 1989, Olson 1989). Island species are more
susceptible to environmental stressors that cause extinctions as a result of their
small population sizes and limited habitat availability. In addition, island
species have adapted in isolated environments making them particularly
vulnerable to impacts from invasive species (Diamond 1985, 1989, Olson 1989).
It
is widely accepted that the natural world is facing a very high rate of species
extinction (Raup 1988), that most recent extinctions can be directly attributed
to human activity (Diamond 1989), and that for ethical, cultural, aesthetic,
and economic reasons this current rate of extinction is cause for considerable
concern (Ehrlich 1988, Ledec and Goodland 1988). One of the major worldwide
causes of anthropogenic extinctions is the introduction of invasive species. Of
the 245 recorded animal species extinctions since 1500, 75% were species
endemic to islands (World Conservation Monitoring Centre 1992). Invasive
species were at least partially responsible for a minimum of 54% of documented
island extinctions, based on the 170 island species for which the cause of
extinction is known (Ricketts et al. 2005).
Benefits
of Eradicating Invasive Rodents
The
effects of invasive species on islands accounts for 80% of all species
extinctions recorded so far. Half of these recorded extinctions were caused by
invasive alien vertebrates (IAV) such as rats, mice, pigs, goats, etc. Rodents
(rats and mice), the most prolific of all invasive vertebrates, are estimated
to have been introduced to more than 80% of the world’s islands as the result
of human activities. Invasive species continue to invade new islands today with
the ever-increasing movement of people and goods around the world. When
introduced to islands, invasive species upset an island’s natural equilibrium
and severely impact native plants and animals that lack adaptations to protect
themselves from the intruders. There is a relatively simple, efficient, and
cost effective solution to this island-species extinction crisis: when invasive
species are removed from islands, native plants, animals, and ecosystems
recover with little or no additional intervention. Combined with effective
biosecurity, the eradication of invasive species is one of the most effective
ways to protect threatened island biodiversity.
As
a consequence of pioneering rodent eradication efforts in New Zealand during
the 1970’s, eradication projects have successfully removed rodent from 571
islands in more than 50 countries around the world (Howald et al. 2007, Keitt
et al. 2011). Moreover, there have been 19 successful rodent eradications in
the United States (Keitt et al. 2011). These successes have invariably resulted
in species and ecosystem recovery and almost certainly saved some species from
extinction (Bellingham et al. 2010). For example the successful eradication of
black rats (Rattus rattus) from
Anacapa Island (California, Channel Islands) more than 10 years ago resulted in
an increased abundance of the Scripps murrelet (Synthliboramphus scrippsi) and the reemergence of the rare ashy
storm-petrel (Oceanodroma homochroa) (http://www.nps.gov/chis/naturescience/restoring-anacapa-island-sea-bird-habitat.htm).
In the last twenty years, eradication of rodents from islands has become one of
the most effective and powerful tools to prevent extinctions and restore ecosystems
(Carrion et al. 2011). Since eradication projects are logistically complex,
expensive, and controversial, they require a solid foundation of operational,
legal, administrative, and communications support to ensure the successful
removal of the target population (Morrison et al. 2011).
The
Need to Streamline
The
successful eradication of black rats from Anacapa in 2002 was the first-ever
invasive rodent eradication from an entire island where an endemic rodent was
present and the first aerial application of a rodenticide in North America (Howald
et al. 2009). This conservation success sparked a wave of rodent eradication
efforts on federally owned islands in the United States. The science illustrating
the need for rodent eradications and the benefits of rodent removal to island
ecosystems has been well documented. Furthermore, several eradication tools have
been used successful on hundreds of projects around the world with minimal
long-term negative consequences. However, since Anacapa Island was the site of
the first rodent eradication in the US to aerially broadcast rodenticide bait for
eradication purposes, a National Environmental Policy Act (NEPA) analysis was
required. An Environmental Impact Statement (EIS) was prepared along with numerous
state and federal permits. The compliance process was relatively rigorous and
took more than a year and a half to complete, paving the way for subsequent
projects using similar techniques in the US.
Since
the successful removal of rats from Anacapa Island, federal land managers have
worked with eradication experts to plan and implement more than 10 additional
island rodent eradication projects (Keitt et al. 2011). A majority of these
projects successfully eradicated the target species with little to no long-term
negative side effects to island ecosystems including Palmyra Atoll, Mokapu
Island, Egmont Cay, Mokolii Island, and Alau Island. Rats were successfully removed from Rat
Island; however, experts did not anticipate the mortality of over 300
glaucous-winged gulls (Larus glaucescens)
and over 40 bald eagles (Haliaeetus
leucocephalus) from the implementation of the project (Ornithological
Council 2010). Recently, Desecheo Island and Wake Atoll projects were
implemented according to plan; however, on Desecheo the eradication team failed
to fully eradicate the target species, while on Wake the team successfully
eradicated Asian rats (Rattus tanazumi)
but not Polynesian rats (Rattus exulans;
Griffiths 2014).
The
recent mistakes in the US coupled with a growing concern over the use of
rodenticides on the mainland and their negative impacts to wildlife, children,
and pets (Daniels 2013) has complicated the compliance process for projects
that are currently in the planning stages, and as a result these projects are
being held to a higher standard requiring more rigorous analyses, additional
public scrutiny, and supplemental compliance processes. For example, the
proposed mouse eradication on the South Farallon Islands has been in the
planning stages for over 10 years. The additional years of planning are due
to more emerging information about the effects residues after eradication
projects, more information and documentation about non-target take from eradication
projects combined with an increased concern over the potential for a project to
fail as a result of the recent unsuccessful projects. In addition there has
been a surge in stakeholder engagement, agency concern over impacts to
resources, as well as, concerns over losing the use of rodenticides for
invasive rodent management in general. For these reasons, a systematic,
transparent problem oriented approach should be used to identify social and
political constraints, identify areas for programmatic planning solutions, and
provide opportunities for stakeholder engagement in an effort to more
efficiently complete the planning process for conservation purposes. Therefore,
the goal of a the streamlining process should be to increase capacity to better
anticipate risks and mitigate potential impacts, create opportunities to gain understanding
of the project benefits and risks, provide an accurate and complete analysis of
the costs and benefits of a proposed project, and enable stakeholders to make
informed decisions on how and whether a project should proceed, as well as,
outline a clearly defined permitting process.
From Planning to Implementation
The
Role of Environmental Compliance in Project Implementation
An
assessment of environmental impacts under NEPA is required for all activities
that have the potential to cause “significant harm to the human environment” (42
USC 4321-4347). Environmental Impact
Assessment (EIA) is a formal analysis used to forecast the environmental
consequences of any project implemented on federal land. The purpose of
developing a robust EIA is to ensure that any potential problems are identified
and addressed early in the planning and design of a project. In addition, EIA’s
enable decision makers to weigh the environmental costs and benefits of a project
at an early stage (Ingole 2007). NEPA requires federal agencies to consider
environmental issues prior to making any major decisions on projects that have
federal involvement (e.g., funding or permitting). To determine a project's
potential benefit or harm to the environment, NEPA requires an assessment of
environmental impacts and an evaluation of alternatives through the development
of an Environmental Assessment (EA) or EIS (42 USC 4321-4347). In addition, EIA’s
provide the background and evidentiary support needed for other permits that
are typically required for large projects.
The
compliance process can take anywhere from 2 to 10 years or more to complete for
rodent eradication projects in the United States. Navigating the compliance
process can be quite cumbersome and complicated since the level of detail
required is typically dictated by the perceived risks rather than the actual
biological, social, or economic risks. Stakeholders can play a powerful role in
the outcome of the planning process as NEPA is a procedural law that only outlines
the steps necessary to complete the process, while the courts interpret the
policy and determine the scope of work. Active stakeholders that are not
properly engaged in the planning process can create unanticipated regulatory
requirements resulting in projects that are often behind schedule and over
budget. For these reasons, agency consultation and stakeholder engagement should
be incorporated into the early phases of planning and continued throughout the
compliance process. Furthermore, stakeholders that are engaged in the planning
process are less likely to seek injunctions, require additional analyses, or
disseminate misinformation (Clark 2002).
NEPA
Analysis
The
National Environmental Policy Act (NEPA) of 1970 was the first law written to establish
a broad national framework for environmental protecting. The basic premise of NEPA
is to ensure that the federal government properly considers the environment
prior to initiating any major federal action that has the potential to significantly
affect the environment (42 U.S.C. § 4321 et seq.). NEPA analysis includes the
completion of either an EA or an EIS depending on the predicted affects to the
environment, the economy, and cultural and historic resources.
An
EA as described in Section 1508.9 of CEQ's NEPA Regulations is a concise public
document that has three defined functions including providing sufficient evidence
and analysis to determine if an EIS is necessary, acting as the agency’s
compliance analysis if an EIS is unnecessary, and facilitating the preparation
of an EIS (EPA 2014). Since the EA is a
concise document, it should not contain long descriptions or detailed data
which the agency may have gathered. Rather, it should contain a brief
discussion of the need for the proposal, alternatives to the proposal, the
environmental impacts of the proposed action and alternatives, and a list of
agencies and individuals consulted -- Section 1508.9(b). Agencies should make
the Finding of No Significant Impact (FONSI) and EA available for 30 days of
public comment and review before taking action -- Section 1501.4(e)(2). (March
16, 1981 – NEPA's 40 Most Asked Questions).
An
EIS, on the other hand, is a detailed environmental analysis that serves to assure
the public and permitting agencies that the policies and goals defined in NEPA
are incorporated by federal agencies into planning decisions. EISs are
generally prepared for projects that are likely to have significant
environmental impacts. The EIS should provide a discussion of potential environmental
impacts and a reasonable range of alternatives (including a No Action
alternative) designed to meet the goals and objectives of the project, as well
as avoid or minimize adverse impacts and enhance the quality of the human
environment. Agencies should allow at least a 45-day comment period for Draft
EISs and a 30-day review period for Final EISs (EPA 2014). The EIS process is
the more streamlined approach for rodent eradication since the majority of
recent projects have come under heavy public scrutiny over the use of
rodenticides, the ability to successfully eradicate the target species, and the
perceived risks to non-target species and the marine environment.
Rodent
eradication projects are often perceived to have significant impacts to
biological, social, or economic resources regardless of the actual long term
risks from the operation. For this reason, it is recommended to proceed with a
Draft EIS and subsequently to convert the document to a Finding of No
Significant Impact (FONSI) if impacts are determined not to be significant with
appropriate mitigation. The clear advantage to this method is that a lot of
time, money, and other resources can be saved by avoiding a two-step EA-EIS
process, if an EIS is determined to be required. Similarly, if the EIS analysis
illustrates that there are no potential significant affects, a FONSI can be
used as the final decision document. Moreover, starting with an EA and then
determining that there are likely to be significant issues that require the
preparation of an EIS, would entail starting from the beginning of the EIS
process with public scoping. This can add anywhere from one to five additional
years of planning to the process (Eccleston 2008). The proposed mouse
eradication on the Farallon Islands began as an EA; however, after several
years and multiple public meetings it was determined that an EIS would need to
be prepared requiring FWS to begin with public scoping and adding at least 3
additional years to the planning process.
Agency
and Stakeholder Engagement
Environmental
problems, like introduced rodents on islands, and subsequent eradications are
often complex, multi-scale issues that affect a large array of stakeholder and
agencies. Additionally, most projects have a great deal of uncertainty
associated with the outcome of the operation since it is difficult to
accurately predict conservation benefits from large scale ecosystem wide
projects. As a result, projects of this capacity require transparent
decision-making, early and ongoing outreach with relevant stakeholders, and the
ability to be flexible to changing circumstances (Reed 2008). Furthermore, Reed
2008 recommends that “participation should be considered as early as possible
and throughout the process, representing relevant stakeholders systematically”
to avoid unanticipated outcomes.
Stakeholder
engagement includes outreach and communication with permitting agencies,
interested parties, and relevant interest groups. Early engagement with
permitting agencies provides an opportunity to determine the information, data,
and field trials needed to issue a permit, as well as create an inclusive
atmosphere that promotes collaboration and support for the project. Early
engagement with interest groups will help identify the public’s perceived risks
of the project as they are usually different than the actual biological,
economic, or social risks of the operation. By engaging with stakeholders early
in the process it is possible to address the public’s specific concerns, allow
them to feel directly involved in the process, gain the public’s trust,
potentially avert the spread of misinformation, and clarify technical aspects
of a project that are difficult to understand. In general, the more engaged
agencies and the public are in the planning process the more likely that
controversial issues can be resolved without the threat of unanticipated
outcomes like additional field trials, more in depth impacts analysis,
injunctions, or denial of a permit.
The
Need to Streamline Compliance
Streamlining
is defined by Merriam-Webster’s online dictionary as being stripped of
nonessentials, effectively integrated, and brought up to date. Streamlining
compliance for rodent eradications is intended to make the process more
efficient and effective by decreasing constraints; however, it is not a method
to bypass the process. In fact, the importance of strict adherence to
compliance and regulatory process cannot be understated (Morrison et al. 2011).
The idea is that by thinking about rodent eradications globally and identifying
programmatic solutions, decision makers will be able to tease out areas that
can be streamlined in a manner that accelerates the process for specific
projects.
This
review covers six approaches to streamline compliance for rodent eradications
that together will result in fewer roadblocks to conservation. Some of the
approaches are intended to be preventative measures that can help decrease the
likelihood of a long drawn out court battle, while others are approaches are
intended to simplify the process. An integrated approach to streamlining will
ultimately lead to a more holistic planning process for rodent eradication projects
in the US, while enabling individual projects to get through the compliance
phase and into the operational phase in a more timely and efficient manner. The
following is a summary of the six recommended approaches to streamlining with a
description of the benefits of employing each approach:
1.
Identify
programmatic planning and permitting opportunities that will increase
efficiency by:
a.
Reducing
redundancy;
b.
Decreasing
the planning timeline and budget; and
c.
Increasing
continuity between projects.
2.
Identify
and understand social and political constraints that can be incorporated into
the planning process to:
a.
Minimize
the risk of controversial law suits or injunctions;
b.
Identify
concepts that require clarification to gain support for the project;
c.
Provide
stakeholders with an opportunity to contribute to the planning and decision
making of a project; and
d.
Ensure
that social and political constraints are included and evaluated in the
planning process.
3.
Develop
a rigorous NEPA document that incorporates all of the social, environmental, and
economic impacts while providing plenty of opportunities for public involvement
by:
a.
Producing
a document that can stand up to public and political scrutiny;
b.
Using
NEPA as a method to minimize the risk of injunction, negative public and agency
comments that can require additional document drafts, analyses, or field
trials; and
c.
Applying
the Precautionary Principle by planning for a worst case scenario.
4.
Strive
for expert consensus within and among the eradication and planning community
by:
a.
Engaging
experts in the early stages of planning to build consensus for the preferred
eradication tools, non-target mitigation strategies, and to identify additional
permits that may be needed;
b.
Developing
consensus will build confidence in the proposed operation with stakeholders;
and
c.
Adding
continuity between projects by acknowledging the lessons learned from each
additional project.
5.
Be
transparent during planning, outreach, and document developing to:
a.
Decrease
the appearance of impropriety;
b.
Accurately
portray the expected impacts from the alternatives;
c.
Provide
as much detail as possible without restricting the ability to adaptively manage
the operation;
d.
Provide
an opportunity to gain buy-in and trust from stakeholders; and
e.
Reduce
the chance of injunction or law suit.
6.
Engage
all stakeholder by:
a.
Identifying
all relevant stakeholders;
b.
Ensuring
that the neglected perspective is included in planning;
c.
Engaging
stakeholders early and often during the planning process; and
d.
Decreasing
the risk of appearing biased or pre-decisional.
How can we streamline?
The
underlying premise behind all rodent eradications is to remove 100% of the
target species, while having a minimal effect on other non-target resources.
The methods used to eradicate rodents, while they can be controversial in
nature, have proven to effectively eradicate the target species with minimal
non-target impacts (Howald et al. 2007). Additionally, since the island
resources from project to project vary, the nature of the concerns over the
implementation of the operation and the required permits are fairly standard.
For these reasons, finding programmatic solutions that can be applied broadly
are ideal for these types of projects particularly in light of the fact that
the same federal permitting agencies are involved in all US based projects.
As
an example, the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA)
requires that all pesticides obtain a prescriptive use label that specifies the
exact uses of the product, how it can be delivered, and restricted uses. Once a
‘parent label’ has been registered with the EPA, any project that complies with
the restrictions listed on the label can obtain and use the product without any
additional permitting under FIFRA. Furthermore,
if a project specific label is needed for a particular project, a ‘supplemental
label’ can be obtained without the need to re-register the product.
It
is fairly easy to obtain a supplemental label for a project using a product
that has been registered under FIFRA because all of the scientific evidence
needed to regulate the product has already been reviewed; therefore,
practitioners only need to justify the unique aspects of a project to obtain
the supplemental label. The Palmyra Atoll rat eradication would have surely
failed had the project team not obtained a supplemental label allowing the team
to increase the application rate in order to account for nonlethal primary
consumption by crabs. In addition without consulting with other eradication and
island experts early in the process, it would have been much more difficult to
obtain consensus for the operational plan to eradicate rats from Palmyra Atoll,
which was essential for EPA to issue the supplemental label.
Another
programmatic solution that has already been developed is a Special Purpose Permit
under the Migratory Bird Treaty Act (MBTA) that allows for the take of MBTA listed
species if the purpose of the operations is intended to result in species
conservation. Prior to 2009 the US Fish and Wildlife Service (FWS) did not
issue any incidental take permits for listed species. However, after the take
of listed birds from the Rat Island eradication in 2008 (Ornithological Council
2010), the FWS began issuing take permits for eradication projects since the
goal of these projects was to benefit listed species in the long-term (Kurth
2010).
In
addition to programmatic solutions, compliance processes can be implemented
more efficiently by developing robust NEPA analyses that clearly states the
purpose and need for the project, evaluates a reasonable range of alternatives,
fully assesses potential impacts and mitigation activities, and actively engages
the public and experts throughout the process. The Anacapa Island rat
eradication was the first aerial rodent eradication in the US. For this reason,
the National Park Service (NPS) developed an EIS and conducted several field
trials and risk assessments to identify the potential risk to the islands
resources and develop an operational protocol to target 100% of the rats on the
island. Despite all of the compliance effort and public involvement, the NPS
was sued by an interest group seeking an injunction to halt the project. Since
the EIS was well developed, fulfilled the procedural obligations of NEPA, and
was supported by eradication experts the NPS was able to win the court case and
implement the project on schedule due to the rigor in the compliance process
(Howald et al. 2005). Another notable example stems from the pig eradication
conducted on Santa Cruz Island, CA in 2005 where five legal challenges were
brought to the courts with allegations that the EIS inadequately evaluated the
risk to the islands species. The project
team had developed an incredibly robust NEPA analysis that was supported by a
team of experts and was able to withstand all five legal challenges without the
need for any additional analysis (Morrison et al. 2011).
Along
with developing a robust NEPA analysis, it is essential to include an
assessment of the social and political environment to better understand the
social conditions in the region, the underlying political concerns, as well as
identify the perceived risks of the problem. Environmental problems, including
invasive species management, are complex and dynamic issues requiring flexible,
transparent decision-making that accounts for the diversity of values in the
region, and identifies any gaps in knowledge of the different stakeholders
(Reed 2008). Failure to assess stakeholder concerns could result in public relations
issues, additional analyses, law suit, or injunction. For example, the planning
for the proposed mouse eradication on the Farallon Islands was initiated prior
to the implementation of the Rat Island, Palmyra Atoll, and Desecheo Island rat
eradications when there was far less public scrutiny over the implementation of
rodent eradications. However, the Rat Island rat eradication resulted in the
unanticipated mortality of over 300 glaucuous-winged gulls (Larus glaucescens) and over 40 bald eagles
(Haliaeetus leucocephalus), the Palmyra
Atoll rat eradication resulted in unexpected mortality of a small number of
mullets in the shallow lagoon, and the Desecheo Island rat eradication failed
to successfully remove all individuals from the island. Subsequently, after these
projects were completed, the public and permitting agencies began to look more
closely at how rodent eradications were being implemented in the US, as well as
the potential impacts to non-target species from the operation. The original EA
that was developed for the proposed mouse eradication on the Farallon Islands
was deemed to be inappropriate and as a result an EIS was developed along with
several additional modeling efforts, field trials, and alternatives analyses that
were needed to complete the compliance process.
Conclusion
Natural
resource professionals manage large complex problems that are extremely
dynamic, include both scientific and non-scientific issues, and are often
limited by the perceived risks of the interested stakeholders. Problems related
to invasive species management demand responses that are not conventional, yet
are highly effective at eradicating the target species. The unconventional
nature of eradication operations coupled with the social and political constraints
associated with managing invasive species make planning and implementing
eradications extremely difficult. In many cases it is difficult to analyze and
solve the problem due to the complex, competing interests of a diverse group of
stakeholders (Clark 2002). Moreover, the overarching regulatory environment
exacerbates the conflict by requiring stakeholder engagement and regulatory
oversight from permitting agencies. For these reasons the compliance process
for rodent eradications is intended to provide the framework to assess
alternatives, identify potential impacts, and actively engage with
stakeholders.
After
reviewing the planning documents for several of the most recent rodent
eradication projects planned in the US, we identified areas where the process
could be streamlined. Streamlining is a
process that can be achieved by identifying programmatic solutions,
understanding social and political constraints, and developing a robust,
transparent assessment of a range of alternatives. The importance of the
compliance process cannot be overstated. Streamlining environmental compliance
for rodent eradications can help practitioners complete their compliance
obligation in a timelier manner while maintaining environmental safeguards. Although each island is unique, many of the
required regulatory hurdles including NEPA, Endangered Species Act, Clean Water
Act, Coastal Zone Management Act, FIFRA, and the MBTA are relevant to all US
based rodent eradications. Identifying areas to streamline within the required
regulatory framework will make planning more efficient, more cost effective,
and less burdensome. Looking for programmatic solutions, actively engaging with
stakeholders and permitting agencies, developing robust, transparent NEPA documents,
and incorporating social and political constraints into the decision making
process can help promote stakeholder engagement, increase buy-in from the
public and experts, and provide more opportunities to remove invasive rodents
from islands and help prevent extinctions. The key is to think globally but act
locally.
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