|
IV. LINKING SPECIFIC PROBLEMS
|
Although protecting wildlife is popular goal, implementing that goal is often difficult. As the
old saying goes, "to plan is heavenly, but to implement is divine". Even if local residents and officials
understand the basic framework and the workable principles of habitat protection described in
Chapters II and III, if is often unclear how to translate them into an effective set of wildlife protection
programs. The problems are compounded by the fact that wildlife protection is never the only
important goal of the community -- it needs to be balanced and integrated with other objectives.
Sometimes, that means finding the least intrusive way to implement wildlife protection goals. In
addition, wildlife protection almost always involves a discussion about the use of real estate and the
need to protect private property rights. In order to respect competing goals and rights, it is important
that the community understand the different tools that are available to achieve habitat protection.
B. DISTINCTIONS IN SCALE AND LOCATION
The previous sections have distinguished between wildlife protection principles that apply at
the landscape scale (such as a valley, a basin, or a major development site) and those that occur at
the site scale (such as a single lot or a small development area). It is important to understand that the
concepts of landscape scale and site scale planning have different implications depending on where
the planning site is on the rural-urban continuum. That is because the planning concepts of "scale"
and "location" are different.
such as "Rural, Suburban, and Urban"
relate to the question: Where is our planning site located?
In order to develop an effective plan for wildlife habitat protection at the local level, the community needs to take into account both the scale and location of their planning area. Each possible combination of scale and location produces its own distinct mix of opportunities and challenges.
Opportunities include situations where the scale of the planning effort or the location of the land make it relatively easily to achieve one or more of the biological principles discussed in Chapter III. Communities should focus on those opportunities and should ensure that the planning effort does not compromise a principle that is relatively easy to achieve. Just because a principle is relatively easy to achieve in a given situation does not mean that it is not important. Sometimes very basic protections -- such as the preservation of large patches of vegetation and effective buffering of those areas -- can be very important to wildlife. In general, the broadest range of opportunities occurs when the community can design a habitat protection scheme based on landscape scale planning for a rural area. In contrast, the list of opportunities is much shorter when the opportunity is for site scale planning in a heavily developed urban area.
Challenges, on the other hand, are situations where either the small size of the planning area
or the location of the land makes it difficult to achieve one or more of the principles. This does not
mean that the challenge is impossible, just that it may require careful attention or creative thinking
to solve the problem. In general, the list of challenges increases as the scale of the planning decreases
and the land becomes more urban. When planning is limited to a smaller scale site in a developed
urban area, it may be a challenge to implement any of the listed principles. In solving their particular
challenges to wildlife habitat protection, communities should be careful not to compromise or forfeit
those principles that are natural opportunities for the site and that may be easier to sustain over the
long run.
C. THE OPPORTUNITY/CHALLENGE MATRIX
In Chapter III, Tables 4 and 5 listed important biological principles that can help preserve wildlife habitat. Table 7 builds on those principles and summarizes a general set of opportunities and challenges that may present themselves in a wildlife protection effort. Obviously, this breakdown of opportunities and challenges will differ for each community and will change depending on which species of wildlife are targeted for protection. In particular, opportunities and challenges may shift depending on whether large or small species are being targeted, and depending on whether the community is trying to preserve a relatively rare or a relatively common set of species.
Planning in rural areas can be done at either the landscape scale or at the site scale, depending on whether the community is engaged in an area-wide planning effort or is drafting specific design standards for lots and subdivisions. Where the habitat lands have not been badly fragmented, it is important to do both.
In addition, Table 7 shows that planning for suburban areas can also be done at both the landscape scale and the site scale. Often, a community can predict that development will continue to trend outward from developed areas, and can engage in an area-wide protection effort for habitat in growth areas. Just because development has begun to move into an area does not mean that protection efforts are limited to site-scale principles. Although the inner edge of a growth area may have so much existing construction and population that site scale principles are appropriate, the outer edge of the area may be so undeveloped that landscape principles can be effective. This is very important, because suburban areas are the fastest growing areas in the state, as well as in the U.S. as a whole. It is also the area in which potential habitat land is being lost at the fastest rate. Failure to use all of the tools available to protect habitat in suburban areas may have the largest impact on wildlife within a typical planning horizon of twenty years. Planning for wildlife habitat protection in suburban areas may also require the most careful thought -- simply because it is neither urban nor rural. This "in-between" status may make it difficult to determine which landscape and site scale principles will be effective -- but it is essential that the community think through all of the potential principles that may apply.
In urban areas, the opportunities are more limited. This is simply because large patches of native vegetation seldom exist, corridors have already been blocked, and it is unreasonable to expect that natural events such as floods and fires can be allowed to occur where large numbers of people live nearby. Table 7 suggests that landscape scale principles are largely inapplicable to urban areas, and that planning for urban infill projects should focus on site scale principles. In those rare cases where very large areas are available for planning or redevelopment in urban areas (for example, sites over 1,000 or 2,000 acres, such as the Stapleton Airport site in Denver), and potential wildlife connections to other areas have not been irretrievably lost, communities should think of the site in suburban terms and should also attempt to apply landscape principles.
| Table 7: The Opportunity/Challenge Matrix | ||||
| LANDSCAPE SCALE
(Valley or Large Development Site) |
SITE SCALE
(Infill or Small Development Site) | |||
| Opportunities | Challenges | Opportunities | Challenges | |
| RURAL AREA | Maintain Large
Patches Prioritize Species Protect Rare
Maintain Habitat
Protect Regionally
Allow Fire, Flood,
Keep Some Areas
|
Maintain Buffers
Facilitate Wildlife
Mimic Natural
|
Minimize Contact
with Large Predators Control Pet-Sized
| |
| SUBURBAN AREA | Prioritize Species
Protect Rare
Maintain Habitat
|
Maintain Large
Patches Protect Regionally
Allow Fire, Flood,
Keep Some Areas
|
Maintain Buffers
Minimize Contact
|
Facilitate Wildlife
Movement Control Pet-Sized
Mimic Natural
|
| URBAN AREA |
N/A |
N/A |
Maintain Buffers
Facilitate Wildlife
Minimize Contact
Control Pet-Sized
Mimic Natural
| |
A second way to approach wildlife habitat is to think about which specific habitat protection
tools may be applicable at the scale for which planning is taking place. Some tools, -- such as land
purchases or transferrable developments rights programs -- may be more effective when used at the
landscape scale to protect relatively large areas of potential habitat. Other tools, -- such as clustering
or the targeting of required land dedications -- may be more effective when used at the site scale.
Finally, some tools such as zoning and subdivision review standards can be effective at both scales.
Table 8 sets forth a general outline of potential tools and the scale at which they are traditionally used.
It is important to realize, however, that almost all of the listed tools can be used effectively at any
scale with a little creative thinking. Each of the tools listed in Table 8 is described in more detail with
examples in Chapter VI.
E. TOOLS FOR THE LANDSCAPE LEVEL
In general, the tools that will be effective in implementing the landscape scale principles in
Chapter III are those that can address the general location of development areas within an entire
valley or basin. When wildlife protection is addressed at this level, it may require that new
development or significant human activity be excluded from an area. If that area includes all or part
of a private landowner's parcel, then tools that provide compensation to the owner -- in terms of
either money or the ability to develop elsewhere -- may be appropriate. Potential tools include habitat
purchase, transferrable development rights (TDRs), preferential taxation, and limited conservation
development. Protection of large patches of native vegetation and corridors may also require the
creation of new large scale zones or overlay districts, or the use of new subdivision review standards.
Finally, an effective approach to wildlife protection at the landscape scale may require the cooperation
of several different governments in the valley or watershed or range area through the use of
intergovernmental agreements. All of these tools attempt to steer new development activity away
from sensitive areas through constitutional means. They do not attempt to address what the new
development will look like -- just where it will take place. The effective use of any of these tools
should be based on accurate information about vegetation and the known range of the targeted
species, both of which are sometimes available from the Division of Wildlife. If accurate information
is not available from other sources, then such information should be obtained from local knowledge
of wildlife behavior patterns and locations.
F. TOOLS FOR THE SITE LEVEL
Appropriate tools for site scale also address where development occurs, but on a much smaller scale. Instead of answering the question "where are there sensitive patches of vegetation or wildlife corridors in this valley?", they answer the question "where are there opportunities to buffer or connect wildlife-supporting vegetation on this particular property?" Site scale tools also address the question "how can the development be designed and human activity controlled within this area to minimize disturbance to the chosen species?"
Appropriate tools to address these issues include the language of the zoning ordinance, (which controls permissible uses of the land and the size and location of structures on their sites)
| Table 8: The Scale/Tool Matrix. | LANDSCAPE SCALE TOOLS | SITE SCALE TOOLS |
| REGULATORY TOOLS | ||
| Zoning Texts and Maps | X | X |
| Special Overlay Districts | X | X |
| Agricultural and Open Space Zoning | X | |
| Performance Zoning | X | |
| Phasing of Development | X | |
| Subdivision Review Standards | X | X |
| Sanctuary Regulations | X | |
| Urban Growth Boundaries | X | |
| Targeted Growth Strategies | X | |
| INCENTIVE TOOLS | ||
|
Density Bonuses |
X |
X |
|
Clustering |
X | |
|
Transferrable Development Rights |
X |
|
|
Preferential Tax Treatment |
X |
|
| ACQUISITION PROGRAMS | ||
|
Fee Simple Purchase |
X |
X |
| Sellbacks and Leasebacks | X | X |
| Options and Rights of First Refusal | X | X |
|
Easements and Purchases of Development Rights |
X | X |
|
Land Dedications and Impact Fees |
X | |
| DEVELOPMENT AGREEMENTS | X | |
| CONTROL OF PUBLIC INVESTMENTS | X | X |
| TAXING AND ASSESSMENT DISTRICTS | X | X |
| PRIVATE SECTOR INITIATIVES | ||
|
Land Trusts |
X | |
|
Limited Conservation Development |
X | |
|
Industrial Restoration Showcase Projects |
X | |
| INTERGOVERNMENTAL AGREEMENTS | X | |
| EDUCATION, CITIZEN INVOLVEMENT, AND TECHNICAL ASSISTANCE | X | X |
and the subdivision standards (which control the layout of building sites and the amount and location
of land parcels that must be set aside for parks within the development). Zoning and subdivision
controls can also set standards for vegetation, buffering, noise, glare, and the number of domestic
pets, all of which can affect nearby wildlife. Another appropriate tool is clustering, which allows a
landowner to move permitted development density from one portion of the site to another in order
to protect sensitive lands. Development density bonuses are also sometimes included to encourage
such clustering. In contrast to landscape level tools, site level tools seldom attempt to prevent
development or human activity on all of an owner's land -- and so TDR or land purchase tools are
seldom required. Instead, easements or limited conservation development plans may be more
appropriate.
G. EXAMPLES OF PROTECTION PROGRAMS
The use of landscape tools and site scale tools should not be treated as an "either/or" choice.
In many rural and suburban communities, an effective wildlife habitat protection program will include
both types of tools. Set forth below are three hypothetical examples of possible wildlife habitat
protection programs for three types of communities. These examples are not suggested as models,
because the tools appropriate for each community will always be determined by that city or county's
specific wildlife protection goals. Instead, they are presented to show how local communities may
need to pull different landscape scale and site scale tools from Table 8 in order to achieve their goals.
All of the tools listed in these examples are described in more detail in Chapter VI.
1. THE JACKELOPE VALLEY -- A RURAL PROGRAM.
The citizens of Jackelope Valley moved there because they enjoyed watching large game
animals and fishing on the gold medal trout stream that runs through the valley. They have also
learned that the valley contains substantial areas with good habitat for two species of fox that are
common in the valley but relatively rare in their portion of the state. After a thorough planning
process, they decided to adopt a valley-wide habitat protection program to preserve the abundance
and increase the distribution of these species. Their program included the following elements.
Landscape Scale Elements
Site Scale Elements
2. HIDDEN VALLEY RANCH ESTATES -- A SUBURBAN EXAMPLE
Spruceland is a growing Front Range suburb located on land that was formerly agricultural.
There are scattered stands of spruce and other trees, several small streams that were plowed over by
the farmers, and an area of rising terrain leading to a unique "cragrock" formation. Leapfrog
development has resulted in an irregular mixture of developed and undeveloped parcels. The citizens
of Hidden Valley Ranch Estates became concerned that they no longer saw deer on the undeveloped
land or heard songbirds in the morning, and they decided to target those species for protection. They
also noticed that they saw fewer types of small animals around the cragrock area. After reviewing
information about predicted growth for the city and remaining areas of vegetation, they decided that
their goal was to increase the abundance and distribution of mule deer and to preserve a viable
population of songbirds. Their program has the following elements.
Landscape Scale Elements
Site Scale Elements
3. FORT PALMER -- AN URBAN EXAMPLE
Fort Palmer is one of the larger cities in the state and is largely built out. There are still a few significant development parcels on the periphery, however, and continuous infill and redevelopment activity. Citizens still notice significant numbers of small animals such as coyotes and rabbits in the drainageways and along the city's hike/bike trails. There are also significant numbers of ducks and geese that use the city's parks and undeveloped lands as winter habitat. After studying potential wildlife corridors and vegetation, the citizens decided to target these species and to aim at preserving their current numbers. Fort Palmer decided to pursue a site scale strategy and adopted a wildlife habitat protection plan with the following elements.
Site Scale Elements
The examples of Jackelope Valley, Hidden Valley Ranch Estates, and Fort Palmer illustrate several points. First, they show the importance of wildlife planning for the community. None of the three communities would have been able to craft an appropriate plan without first studying the land, the existing wildlife, the regional context, and the opinions of their residents. Second, they show how each community's habitat protection plan is likely to be different. Not only are different species important to different communities, but the preservation goals also differ. Some communities will want to expand the numbers of wildlife, others will focus on increasing the variety of wildlife, and yet others will be satisfied with preserving the types and kinds of wildlife that are already present. Third, the examples show the wide variety of wildlife habitat protection tools that can be used to achieve specific goals. Each of the tools mentioned above -- and many more -- are discussed in Chapters V and VI below. Once again, the package of tools will have to be assembled and tailored to match the specific goals of the community.
| Next Chapter | Table of Contents |