The Florida Land Trust
The Florida Land Trust is an amazing device which offers numerous benefits to property owners. The two reasons it is not used by every investor are that few know much about it and those who know about it do not know where to obtain trust services at a reasonable cost.
Trusts in general go back many hundreds of years and today they offer even more benefits than they did when they were invented. The Florida land trust is a statutory form of the "Illinois-type" land trust which has been used for over a hundred years.
The most important benefits of the land trust are privacy and avoidance of probate. With a land trust, no one needs to know what real estate you own either during your life nor at your death, and by avoiding probate you avoid thousands of dollars in attorney fees and months delay in distribution of your property to your heirs.
By using a land trust with Land Trust Service Corporation as trustee, there will be no public record of your ownership of the real estate in the trust. The public records will list the corporation as trustee, and the tax bill will be sent to the trustee (who will forward it to you for payment). The property will be managed by you or by your agent. Income tax returns will be filed by you in the same way they would for property in your own name.
Over twenty other benefits of using a land trust are listed in the book, Land Trusts in Florida, which you should read if you are planning to use a land trust. Some of the most popular benefits are, keeping the sales price secret, keeping liens and judgments off the property, avoiding a spouse's forced share, and avoiding litigation.
The beneficiary of your trust can be you individually, a corporation, a limited liability company, a partnership or any other legal entity. If you are the beneficiary individually, you can name any other person or entity to immediately become successor beneficiary upon your death. If your company is the beneficiary, you can name a successor in your company papers.
Besides a beneficiary, you can have a director. For example, you can set up a trust in which your children are the beneficiaries (paying the taxes on income) but you are the director. As director you would make all the decisions regarding the property. If you loan someone money you can have them put their property in a land trust and make you the director. Then you could control the property until you were paid in full.
IN THE DISTRICT COURT OF APPEAL OF THE STATE OF FLORIDA
FOURTH DISTRICT JULY TERM 2001
PINECREST LAKES, INC.; and
VILLAS AT PINECREST LAKES
LIMITED PARTNERSHIP,
Appellants,
v.
KAREN SHIDEL,
Appellee.
CASE NO. 4D99-2641
Opinion filed September 26, 2001
Appeal from the Circuit Court for the
Nineteenth Judicial Circuit, Martin County; Larry
Schack, Judge; L.T. Case No. 96-126 CA.
Jack J. Aiello and Ernest A. Cox, III, of
Gunster, Yoakley, Valdes-Fauli & Stewart, P.A.,
West Palm Beach, for appellants.
Richard Grosso, General Counsel, Environmental
& Land Use Law Center, Fort Lauderdale, for
appellee.
Stephen H. Grimes and Lawrence E. Sellers, Jr.
of Holland & Knight, LLP., Tallahassee, for Amici
Curiae, National Association of Home Builders,
Florida Home Builders Association, Florida
Association of Realtors, and Association of Florida
Community Developers, Inc.
Michael L. Rosen, Tallahassee, for Amicus
Curiae, Florida Legal Foundation, Inc.
Terrell K. Arline, Legal Director, Tallahassee,
Thomas G. Pelham, Kenneth J. Goldberg and
Douglas W. Ackerman, Tallahassee, for Amici
Curiae, The Florida Chapter of the American
Planning Association, and 1000 Friends of Florida,
Inc.
C
ORRECTED OPINIONFARMER, J.
The ultimate issue raised in this case is
unprecedented in Florida. The question is whether
a trial court has the authority to order the complete
demolition and removal of several multi-story
buildings because the buildings are inconsistent
with the County’s comprehensive land use plan.
We conclude that the court is so empowered and
affirm the decision under review.
Some twenty years ago, a developer
1 purchaseda 500-acre parcel of land in Martin County and set
out to develop it in phases. Development there is
governed by the Martin County Comprehensive
Plan (the Comprehensive Plan).
2 Phase One ofthe property was designated under the
Comprehensive Plan as “Residential Estate,”
meaning single-family homes on individual lots
with a maximum density of 2 units per acre
(UPA). The Comprehensive Plan provides that
“[w]here single family structures comprise the
dominant structure type within these areas, new
development of undeveloped abutting lands shall
1Originally the developer was Pinecrest Lakes, Inc.,
the entity which planned and built Phases One through
Ten. In 1997, when we reversed the first appeal in this
case for a trial de novo, the corporation transferred title
to Phase Ten to a limited partnership known as The
Villas at Pinecrest Lakes. The trial court substituted the
limited partnership for the corporation as the developer.
Consequently, when we use the term “developer” in
this opinion, we refer either to the corporation or the
limited partnership or both as the context requires.
2
See § 163.3167(2), Fla. Stat. (2000) (“Each localgovernment shall prepare a comprehensive plan of the
type and in the manner set out in this act or shall
prepare amendments to its existing comprehensive plan
to conform it to the requirements of this part in the
manner set out in this part.”).
(2)
be required to include compatible structure types
of land immediately adjacent to existing single
family development.” [e.s.]
Phases One through Nine were developed as
single-family homes on individual lots in very low
densities.
The subject of this litigation, Phase Ten, is a 21-
acre parcel between Phase One and Jensen
Beach Boulevard, a divided highway designated
both as “major” and “arterial.” Phase Ten was
designated by the Comprehensive Plan as
“Medium Density Residential” with a maximum of
8 UPA. The developer sought approval of three
different site plans before finally erecting the
buildings that are the subject of this litigation. In
1988, the developer first sought approval for an
initial scheme of 3-story apartment buildings with
a density of just under 8 UPA. Karen Shidel,
since 1986 an owner of a single-family residence
in the adjoining area of Phase One, along with
other residents, opposed the project proposed by
the developer. This initial site plan for Phase Ten
was approved by the County but never acted
upon.
Five years later the developer changed the
proposed scheme to single family residences, and
the County Commission approved a revised site
plan for 29 single-family homes with a density of
1.37 UPA. Two years after that, however, the
developer again changed its mind and returned to
its original concept of multi-family structures. This
time, the developer sought to develop 136 units in
two-story buildings, with a density of 6.5 UPA.
The County’s growth management staff
recommended that the County Commission
approve this second revised site plan for Phase
Ten. Following a hearing at which a number of
people objected to the proposal, including Shidel,
the County Commission approved the revision and
issued a Development Order
3 for Phase Tenpermitting the construction of 19 two-story
buildings.
Claiming statutory authority, Shidel and another
Phase One homeowner, one Charles Brooks,
along with the Homeowners Associations for
Phases One through Nine, then filed a verified
complaint with the Martin County Commission
challenging the consistency of the Development
Order with the Comprehensive Plan, requesting
rescission of the Development Order.
4 Inresponse to the verified complaint, after a hearing
the County Commission confirmed its previous
decision to issue the Development Order.
Shidel and Brooks then filed a civil action in the
Circuit Court against Martin County under the
same statutory authority.
5 They alleged that the3
See § 163.3164(7) and (8), Fla. Stat. (2000)(“‘Development permit’ includes any building permit,
zoning permit, subdivision approval, rezoning,
certification, special exception, variance, or any other
official action of local government having the effect of
permitting the development of land.… ‘Development
order’ means any order granting, denying, or granting
with conditions an application for a development
permit.”).
4
See § 163.3215(4), Fla. Stat. (2000) (“As a conditionprecedent to the institution of an action pursuant to
this section, the complaining party shall first file a
verified complaint with the local government whose
actions are complained of, setting forth the facts upon
which the complaint is based and the relief sought by
the complaining party. The verified complaint shall be
filed no later than 30 days after the alleged inconsistent
action has been taken. The local government receiving
the complaint shall respond within 30 days after receipt
of the complaint. Thereafter, the complaining party may
institute the action authorized in this section. However,
the action shall be instituted no later than 30 days after
the expiration of the 30-day period which the local
government has to take appropriate action.”).
5
See § 163.3215(1), Fla. Stat. (1995) (“Any aggrievedor adversely affected party may maintain an action for
injunctive or other relief against any local government
to prevent such local government from taking any
action on a development order…which materially alters
the use or density or intensity of use on a particular
piece of property that is not consistent with the
comprehensive plan adopted under this part.”).
(3)
Development Order was inconsistent with the
Comprehensive Plan. The developer intervened.
Shidel and Brooks argued that their statutory
challenge was a de novo proceeding in which the
court should decide in the first instance whether
the Development Order was consistent with the
Comprehensive Plan. Martin County and the
developer argued that the proceeding was in the
nature of appellate review in which the County’s
determination was entitled to deference and the
court should consider only whether there was
substantial competent evidence supporting the
Development Order. Basing its decision solely on
a review of the record created before the County
Commission, the trial court found that the
Development Order was consistent with the
Comprehensive Plan and entered final judgment in
favor of the developer.
At that point, the developer took stock of its
position. It had prevailed before the County
Commission and—at least initially—in the trial
court. Technically, however, its approval for the
project was not final. Developer considered
whether to proceed to construct the buildings or
instead await appellate review of the trial court’s
decision. Ultimately the developer decided to
commence construction, notwithstanding the
pendency of an appeal. Accordingly, it applied for
and received building permits for construction of
Buildings 8, 9, 10, 11 and 12, and started on each
of those buildings while the case was under
consideration in court.
6 When construction wasjust beginning, Shidel and Brooks sent written
notice to the developer of their intention, should
they prove successful in court, to seek demolition
and removal of any construction undertaken while
judicial consideration of the consistency issue was
pending.
Appellate review did not produce the outcome
for which the developer had hoped. In 1997 we
reversed the trial court’s decision that the
County’s consistency determination complied with
the Comprehensive Plan. Poulos v. Martin
County, 700 So. 2d 163 (Fla. 4th DCA 1997).
Specifically, we concluded that section 163.3215
required de novo consideration in the trial court on
the consistency issue. Our opinion explained:
“if section 163.3215 was intended to provide for
the circuit court to conduct an appellate review
by certiorari, then the statutory language
permitting the filing of the action up to 90 days
after the granting of the development order is in
conflict with the 30 day deadline outlined under
the Florida Rules of Appellate Procedure.”
700 So. 2d at 165. We further adopted an analysis
by Judge Wentworth as to the meaning of section
163.3215:
“the…language in the statute…provides only for
a suit or action clearly contemplating an
evidentiary hearing before the court to
determine the consistency issue on its merits in
the light of the proceedings below but not
confined to the matters of record in such
proceedings.”
700 So. 2d at 166 (quoting from Gregory v. City
of Alachua, 553 So. 2d 206, 211 (Fla. 1st DCA
1989) (Wentworth, J., dissenting)). We remanded
the case for a trial de novo and for any
appropriate relief.
On remand, the trial judge
7 proceeded in twos tages: the first stage involved a determination
whether the Development Order was consistent
with the Comprehensive Plan; and the second
stage, which became necessary, addressed the
remedy. While the case was pending on remand,
developer continued with construction. The
County conducted final inspections of Building 11
and 12, issuing certificates of occupancy (CO),
and residents moved into the buildings. At the end
of the consistency phase, the trial court entered a
partial judgment finding that the Development
6We express no view on the propriety of Martin
County issuing building permits while the case was
pending in court.
7The original judge assigned to the case was rotated
into another division, so the case was assigned to a
new judge.
(4)
Order was not consistent with the Comprehensive
Plan. The trial de novo then proceeded to the
remedy.
At the conclusion of the remedy phase, the trial
court entered a Final Judgment. The court found
that the Comprehensive Plan established a
hierarchy of land uses, paying deferenc e to lower
density residential uses and providing protection to
those areas. The “tiering policy” required that, for
structures immediately adjacent to each other, any
new structures to be added to the area must be
both comparable and compatible to those already
built and occupied.
8 The court then foundsignificant differences between the northern tier of
Phase One and the adjacent southern tier of
Phase Ten. The structures in Phase One were
single level, single family residences, while the
structures in Phase Ten were two-story apartment
buildings with eight residential units. Therefore,
the court found, the 8-residential unit, two-story,
apartment buildings in Phase Ten were not
compatible or comparable types of dwelling units
with the single family, single level residences in
Phase One; nor were they of comparable density.
Consequently, the court determined, the
Development Order was inconsistent with the
Comprehensive Plan.
As regards the remedy, the Final Judgment
found no evidence indicating that either Brooks or
the Homeowners Association were damaged by
any diminution in value. The court found that the
Homeowners Association was not a person within
the meaning of section 163.3215(2) and therefore
had no standing to seek relief under section
163.3215. Accordingly, only plaintiff Shidel was
entitled to seek injunctive relief under section
163.3215.
In granting such relief, the court found that the
developer had acted in bad faith. Specifically, the
court found that the developer continued
construction during the pendency of the prior
appeal and continued to build and lease during the
trial—even after losing on the consistency issue.
The court found that the developer “acted at [its]
own peril in doing precisely what this lawsuit
sought to prevent and now [is] subject to the
power of the court to compel restoration of the
status prior to construction.” The relief awarded
was:
(1) the Court permanently enjoined Martin
County from taking any further action on the
subject Development Order for Phase Ten,
other than to rescind it;
(2) the Court permanently enjoined developer
and its successors in interest from any further
development of Phase Ten under the subject
Development Order; and
(3) the Court ordered developer to remove all
apartment buildings from Phase Ten either
through demolition or physic al relocation by a
date certain.
When the Final Judgment was entered, five of the
eight-unit buildings had been constructed in Phase
Ten (Buildings 8-12). Buildings 11 and 12 had
already received their CO’s, and fifteen of their
sixteen units were actually occupied. Building 10
was fully completed and was awaiting final
inspection as of the date the remedies stage of
trial began. Buildings 8 and 9 were 50% and 66%
completed, respectively, also as of that date.
Following the entry of Final Judgment, the
developer filed this timely appeal and moved for
a stay pending review.
9 The trial court granted a8“A project immediately adjacent to lands used or
designated for lower intensity use should be given
lesser density. (1) For that portion of said project
abutting the existing development or area of lesser
density, a density transition zone of comparable
density and compatible dwelling unit types shall be
established [e.s.] in the new project for a depth from the
shared property line that is equivalent to the depth of
the first tier of the adjoining development’s lower
density (i.e. the depth of the first block of single-family
lots).” Comprehensive Plan, § 4-5(A)(2)(b).
9Neither Charles Brooks nor Martin County has
appealed the final judgment, or filed a brief in this
appeal by Karen Shidel.
(5)
stay only as to the demolition order, allowing
lessees to continue in possession of those
apartments in Buildings 9-12 under actual lease
when the trial court entered final judgment, as well
as to those leases in Building 8 in existence as of
the date of filing of the notice of appeal. The
developer was prohibited, however, from entering
into any renewals of existing leases upon
expiration of the original term or any new leases
of any apartments. Upon review, we affirmed the
stay order. We now explain our decision on the
merits.
I. The Consistency Issue
Initially the developer argues that the trial court
erred in the consistency phase by failing to accord
any deference to the County Commission’s
interpretation of its own Comprehensive Plan
when the County approved the second revised site
plan and its multi-story, multi-family buildings.
Conceding that the proceedings are de novo and
that the Development Order is subject to “strict
scrutiny” under the Comprehensive Plan as to the
consistency issue, the developer nevertheless
argues that the courts must bow to the County’s
interpretation of its own Comprehensive Plan and
the application of its many elements to the site
plan. Developer argues that the statutes and
cases accord such deference to a local
government’s interpretation of its own
Comprehensive Plan and that it was reversible
error for the trial court in this case to fail to do so.
In partic ular, developer relies on Southwest
Ranches Homeowners Ass’n v. Broward
County, 502 So. 2d 931 (Fla. 4th DCA 1987), and
B.B. McCormick & Sons, Inc. v. City of
Jacksonville, 559 So. 2d 252 (Fla. 1st DCA
1990). According to developer, these cases
authorize the use of the highly deferential “fairly
debatable” standard of review—customary with
zoning decisions—to land use determinations such
as the issue of consistency in this case. We
disagree.
As we have already seen in this dispute, the
applicable statute provides that:
“[a]ny aggrieved or adversely affected party
may maintain an action for injunctive or other
relief against any local government to prevent
such local government from taking any action on
a development order…which materially alters
the use or density or intensity of use on a
particular piece of property that is not consistent
with the comprehensive plan….”
§ 163.3215(1), Fla. Stat. (2000). This statute
obviously creates an action for an injunction
against the enforcement of a development order,
rather than to carry out such an order. The
statute is aimed at development orders—which, by
their very nature, must have been approved by a
local government—so it is clear that the
Legislature did not mean that local governments or
developers would be the parties seeking injunctive
relief under this provision.
Moreover there is but one basis for issuing the
injunction: that the development order is not
consistent with the Comprehensive Plan to the
detriment of adjoining property owners. Hence
the issuance of an injunction under section
163.3215(1) necessarily requires the judge to
determine in the first instance whether a
development order is consistent with the
Comprehensive Plan. When a statute authorizes a
citizen to bring an action to enjoin official conduct
that is made improper by the statute, and that
same statute necessitates a determination by the
judge in the action as to whether the official’s
conduct was improper under the statute, as a
general matter the requirement for a determination
of the propriety of the official action should not be
understood as requiring the court to defer to the
official whose conduct is being judged. While the
Legislature could nevertheless possibly have some
reason to require some deference to the officials
whose conduct was thus put in issue, we would
certainly expect to see such a requirement of
deference spelled out in the statute with
unmistakable clarity. Here it is not a question of
any lack of clarity; the statute is utterly silent on
the notion of deference. It is thus apparent that
(6)
the structure and text of the statute do not
impliedly involve any deference to the decision of
the county officials. So we necessarily presume
none was intended.
10Section 163.3194 requires that all development
conform to the approved Comprehensive Plan, and
that development orders be consistent with that
Plan.
11 The statute is framed as a rule, acommand to cities and counties that they must
comply with their own Comprehensive Plans after
they have been approved by the State. The
statute does not say that local governments shall
have some discretion as to whether a proposed
development should be consistent with the
Comprehensive Plan. Consistency with a
Comprehensive Plan is therefore not a
discretionary matter. When the Legislature wants
to give an agency discretion and then for the
courts to defer to such discretion, it knows how to
say that. Here it has not. We thus reject the
developer’s contention that the trial court erred in
failing to defer to the County’s interpretation of its
own comprehensive plan.
Before we proceed to assess the trial court’s
determination on the consistency issue, we pause
to consider the history of the land development
statutes. The State of Florida did not assert
meaningful formal control over the explosive and
unplanned development of land in this state until
the passage of the first growth management
statute, the Local Government Comprehensive
Planning Act of 1975. Chapter 75-257, Laws of
Fla. (the 1975 Act). The 1975 Act forced
counties and cities to adopt comprehensive plans,
but they were left to interpret such plans for
themselves, largely free from effective oversight
by the state. See, e.g., City of Jacksonville
Beach v. Grubbs, 461 So. 2d 160, 163 (Fla. 1st
DCA 1984) (determination of when to conform
more restrictive zoning ordinances with
Comprehensive Plan is legislative judgment to be
made by local governing body, subject only to
limited judicial review for patent arbitrariness).
The requirement of adopting a Comprehensive
Plan was, therefore, only a small step. Moreover
nothing in the legislation required local
governments to comply with their own
Comprehensive Plans or that all development be
consistent with the Plan.
By the early 1980’s it was widely recognized
10To illustrate the point, we draw an analogy. The
action by a county approving a development order
could fairly and logically be compared to the actions of
administrative agencies generally. Thus we might
contrast section 163.3215(1) with comparable provisions
of the Administrative Procedures Act. Section 120.68
generally grants parties in agency proceedings access
to a court after the agency has finally acted. Section
120.68(4), however, limits review to the record in
agency. There is no similar provision in section
163.3215. Moreover section 120.68(7) spells out in
precise detail exactly what the reviewing court can do.
Among its provisions is the following:
“The court shall remand a case to the agency for
further proceedings consistent with the court’s
decision or set aside agency action, as appropriate,
when it finds that … (b) The agency’s action
depends on any finding of fact that is not supported
by competent, substantial evidence in the record of
a hearing conducted pursuant to ss. 120.569 and
120.57; however, the court shall not substitute its
judgment for that of the agency as to the weight of
the evidence on any disputed finding of fact … (e)
the agency’s exercise of discretion was: 1. outside
the range of discretion delegated to the agency by
law; 2. inconsistent with agency rule; 3. inconsistent
with officially stated agency policy or a prior agency
practice, if deviation therefrom is not explained by the
agency; or 4. otherwise in violation of a
constitutional or statutory provision; but the court
shall not substitute its judgment for that of the
agency on an issue of discretion.” [e.s.]
§ 120.68(7), Fla. Stat. (2000). There is nothing even
remotely comparable in section 163.3215.
11
See § 163.3194(1)(a), Fla. Stat. (2000) (“After acomprehensive plan…has been adopted in conformity
with this act, all development undertaken by, and all
actions taken in regard to development orders by,
governmental agencies in regard to land covered by
such plan or element shall be consistent with such plan or element as adopted.”). [e.s.]
(7)
that the 1975 Act was proving ineffectual in
regulating Florida’s development. See Reid
Ewing, Florida’s Growth Management
Learning Curve, 19 V
A. ENVT’L. L. J. 375(2000). The lack of state control over
interpretation of the Comprehensive Plan was
often cited as a serious deficiency. As one such
criticism described the situation:
“[f]rustration grew at the state level as well.
Lacking the actual power to approve or
disapprove local planning decisions, state and
regional planners could not effectively
coordinate and oversee local planning and
regulation. Local governments changed their
plans ‘willy-nilly virtually every time a city
council or county commission met...’ ”
John M. DeGrove, State and Regional Planning
and Regulatory Activity: The Florida
Experience and Lessons for Other
Jurisdictions, C390 ALI– ABA 397, 428 (1994).
For another thing, the 1975 Act was criticized
for failing to give affected property owners and
citizen groups standing to challenge the land
development decisions of local governments on the
grounds that they were inconsistent with the
Comprehensive Plan. The standing issue was
considered in Citizens Growth Management
Coalition of West Palm Beach Inc. v. City of
West Palm Beach, 450 So. 2d 204 (Fla. 1984)
(CGMC). CGMC involved a challenge by a
citizens group to a local decision to allow the
construction of a large scale residential and
commercial complex. The court began by
referring to Renard v. Dade County, 261 So.2d
832 (Fla. 1972), holding that standing to challenge
local development decisions was limited to the
highly deferential “fairly debatable” standard.
Affected property owners in the vicinity of new
development had no standing to seek enforcement
of local comprehensive plans unless they could
“prove special damages different in kind from that
suffered by the community as a whole.” 261 So.
2d at 834. The CGMC court determined that the
1975 Act did not change these rules on standing.
450 So. 2d at 208. The court reasoned that
because the 1975 Act “did not specifically address
the question” of standing, the statute was not
meant to alter the common law standing
requirements set forth in Renard. 450 So. 2d at
206-07.
Again, to return to the criticism, this limitation on
standing to enforce local planning laws resulted in:
“a failure to conform development decisions to
the plan based upon the fact that citizens lacked
standing to challenge development orders for
lack of consistency with the comprehensive
plan.”
James C. Nicholas & Ruth L. Steiner, Growth
Management and Smart Growth in Florida, 35
W
AKE FOREST L. REV. 645, 657 (2000)(quotingDaniel W. O'Connell, Growth Management in
Florida: Will State and Local Governments Get
Their Acts Together?, F
LORIDA ENVT’L &U
RBAN ISSUES, 1-5 (June 1984)). If affectedproperty owners in the area of newly permitted
development could not challenge a project on the
grounds that it would be inconsistent with the
Comprehensive Plan, that eliminated the only real
check on local government compliance—a
challenge by those most directly affected by a
proposed development.
The growing pressure for a fundamental change
in the growth management law is reflected in the
following statement made just prior to the
Legislature’s adoption of the current law in 1985:
“In response to this lack of citizen standing, a
citizen initiative began last year and thousands of
signatures were collected around the state to
bring the standing issue to a referendum vote.
The petition specific ally calls for a referendum
on the issues of giving citizens a right in the state
constitution to environmental health and welfare
and providing them with legal standing to sue if
government at the local, regional, or state level
is not doing its job.
“That initiative fell just a few thousand
signatures short of the required number for
qualifying for a referendum in 1984. However,
(8)
the initiative is continuing, and I feel confident that
the issue will be brought to the voters of the state
in 1985 unless the legislature addresses the issue
more effectively than it did last year.”
Kathleen Shea Abrams, An Environmental Word,
1 J. L
AND USE & ENVT’L LAW 155, 159 (1985).Clearly the pressure from a “civically militant
electorate” was growing, and the elected
representatives took notice of it. The result was
the Growth Management Act of 1985. Chap. 85-
55, Laws of Fla. This is essentially the statute we
have today, parts of which have been cited in
preceding paragraphs.
12 Its most importantprovision for our purposes was section 163.3215,
the provision used by Shidel to bring this action
into court.
In Southwest Ranches, we observed that
section 163.3215 had liberalized standing
requirements and demonstrated “a clear legislative
policy in favor of the enforcement of
comprehensive plans by persons adversely
affected by local action.” 502 So. 2d at 935. In
Parker v. Leon County, 627 So. 2d 476, 480 (Fla.
1993), the court held that “the legislature enacted
section 163.3215 to ensure the standing for any
person who ‘will suffer an adverse effect to an
interest protected ... by the ... comprehensive
plan.’ ” 627 So. 2d at 479. The Parker court
quoted with approval the above passage from
Southwest Ranches. 627 So. 2d at 479. See also
Putnam County Envt’l Council, Inc. v. Board of
County Comm’rs of Putnam County, 757 So. 2d
590, 593 (Fla. 5th DCA 2000) (“That standard
changed, however, with the 1985 adoption of
section 163.3215, which liberalized the standing
requirements and ‘demonstrat[ed] a clear
legislative policy in favor of the enforcement of
comprehensive plans by persons adversely
affected by local action.’”). Thus, the criticism
described above certainly was of great influence
in the 1985 Legislature’s formulation of the new
standing provision. Affected citizens have been
given a significantly enhanced standing to
challenge the consistency of development
decisions with the Comprehensive Plan.
The Growth Management Act of 1985 was
discussed in what is now recognized as the most
significant land use decision by the supreme court
in the past decade, namely Board of County
Commissioners of Brevard County v. Snyder,
627 So. 2d 469 (Fla. 1993). Snyder involved a
parcel then zoned only for single family homes and
a proposed development of 5-6 units. The
proposal also necessarily required a change of
zoning. After substantial opposition, and in spite of
a favorable staff recommendation, the County
voted to deny the request without giving any
reasons. Certiorari was denied in the circuit court,
one judge dissenting. The Fifth District held that
rezoning actions entailing the application of a
general rule or policy to specific individuals,
interests, or activities are quasi-judicial in nature
and should be subjected to a stricter standard of
judicial review. The court found that the proposed
site plan was consistent with the Comprehensive
Plan, that there was no evidence supporting the
denial of any necessary rezoning, and that the
denial of the request without giving any reasons
was arbitrary and unreasonable.
After granting review, the supreme court was
first concerned with the level of review given by
the courts to such proceedings. The county took
the position that it had been faced with primarily a
legislative judgment because the landowner sought
rezoning. As the court noted:
“Both federal and state courts adopted a highly
deferential standard of judicial review early in
the history of local zoning. In Village of Euclid
v. Ambler Realty Co., 272 U.S. 365 (1926), the
United States Supreme Court held that ‘[i]f the
validity of the legislative classification for zoning
purposes be fairly debatable, the legislative
judgment must be allowed to control.’ This
Court expressly adopted the fairly debatable
principle in City of Miami Beach v. Ocean &
Inland Co., 147 Fla. 480, 3 So.2d 364 (1941).”
12
See supra notes 2, 3, 4 and 5 and accompanyingtext.
(9)
[c.o.]
627 So. 2d at 472. The court went on to note,
however, that this tolerant form of judicial review
had not proved satisfactory:
“Inhibited only by the loose judicial scrutiny
afforded by the fairly debatable rule, local zoning
systems developed in a markedly inconsistent
manner. Many land use experts and
practitioners have been critical of the local
zoning system. Richard Babcock deplored the
effect of ‘neighborhoodism’ and rank political
influence on the local decision-making process.
Richard F. Babcock, The Zoning Game (1966).
Mandelker and Tarlock recently stated that
‘zoning dec isions are too often ad hoc, sloppy
and self-serving decisions with well-defined
adverse consequences without off-setting
benefits.’ Daniel R. Mandelker and A. Dan
Tarlock, Shifting the Presumption of
Constitutionality in Land-Use Law, 24 U
RB.L
AW. 1, 2 (1992).”627 So. 2d at 472-73.
The court explained that in Florida the 1975 Act
“was substantially strengthened by the Growth
Management Act [of 1985].” 627 So. 2d at 473.
After analyzing various provisions of the Growth
Management Act of 1985, the court stated:
“We also agree with the court below that the
review is subject to strict scrutiny. In practical
effect, the review by strict scrutiny in zoning
cases appears to be the same as that given in
the review of other quasi-judicial decisions. See
Lee County v. Sunbelt Equities, II, Ltd.
Partnership, 619 So.2d 996 (Fla. 2d DCA1993)
(The term ‘strict scrutiny’ aris es from the
necessity of strict compliance with
comprehensive plan.). This term as used in the
review of land use decisions must be
distinguished from the type of strict scrutiny
review afforded in some constitutional cases.
Compare Snyder v. Board of County
Comm'rs, 595 So.2d 65, 75-76 (Fla. 5th
DCA1991) (land use), and Machado v.
Musgrove 519 So.2d 629, 632 (Fla. 3d
DCA1987), review denied, 529 So.2d 693
(Fla.1988), and review denied, 529 So.2d 694
(Fla.1988) (land use), with In re Estate of
Greenberg, 390 So.2d 40, 42-43 (Fla.1980)
(general discussion of strict scrutiny review in
context of fundamental rights), appeal
dismissed, 450 U.S. 961 (1981), Florida High
Sch. Activities Ass'n v. Thomas, 434 So.2d 306
(Fla.1983) (equal protection), and Department
of Revenue v. Magazine Publishers of
America, Inc., 604 So.2d 459 (Fla.1992) (First
Amendment).” [e.s.]
627 So. 2d at 475.
In the foregoing quotation the supreme court
drew a distinction between the use of strict
scrutiny in land use cases and its use in other
contexts. The court approved the analyses of the
Fifth District in Snyder and the Third District in
Machado v. Musgrove, 519 So. 2d 629, 632 (Fla.
3d DCA 1987), review denied, 529 So. 2d 693
(Fla.), review denied, 529 So. 2d 694 (Fla. 1988),
regarding land use decisions. These courts
explained that strict scrutiny of local government
development orders is necessary to insure that the
local governments comply with the duty imposed
by section 163.3194 to make decis ions consistent
with the Comprehensive Plan. In discussing the
difference between a developer aggrieved by a
land use decision of local government and an
affected property owner in the vicinity aggrieved
by a proposed new development, the Snyder court
emphasized that section 163.3215 “provides a
remedy for third parties to challenge the
consistency of development orders.” 627 So. 2d
at 475.
As one pair of writers put it, “Snyder changed
the rules of the game for local government land
use approvals.” John W. Howell & David J.
Russ, Planning vs. Zoning: Snyder Decision
Changes Rezoning Standards, F
LA. B.J., May1994, at 16. And another pair noted:
“The easygoing ‘fairly debatable’ test for sitespecific
rezonings was abandoned and the ‘strict
scrutiny’ standard was adopted for the review
of development orders under a county’s
(10)
comprehensive master plan.”
Lucia A. Dougherty & Elliot H. Scherker, Rights,
Remedies, and Ratiocination: Toward a
Cohesive Approach to Appellate Review of
Land Use Orders After Board of County
Commissioners v. Snyder, 24 S
TET. L. REV. 311,312 (1995). In light of this history, deferential
review of the kind advocated by developer here is
no longer the rule after Snyder.
Under section 163.3215 citizen enforcement is
the primary tool for insuring consistency of
development decisions with the Comprehensive
Plan. Deference by the courts—especially of the
kind argued by the developer in this case—would
not only be inconsistent with the text and structure
of the statute, but it would ignore the very reasons
for adopting the legislation in the first place.
When an affected property owner in the area of a
newly allowed development brings a consistency
challenge to a development order, a cause of
action—as it were—for compliance with the
Comprehensive Plan is presented to the court, in
which the judge is required to pay deference only
to the facts in the case and the applicable law. In
light of the text of section 163.3215 and the
foregoing history, we reject the developer’s
contention that the trial court erred in failing to
defer to the County’s interpretation of its own
Comprehensive Plan.
Having thus decided that the trial court was
correct in failing to accord any particular
deference to the Martin County Commission in its
interpretation of the Comprehensive Plan, we now
proceed to consider the court’s determination on
the consistency issue. The trial court explained its
decision as follows:
“The primary claim by [plaintiffs] is that the
juxtaposition of multi-story, multi-family
apartments in Phase 10 directly next to the
single family homes in Phase 1 violates a
number of provisions in the Comprehensive
Plan. The provision of the Comprehensive Plan
that is central to their argument is section 4-
5(A)(2)(b), known as the ‘tiering policy.’ [see n.
6, above]
“The tiering policy was added to the
Comprehensive Plan … to address how
development would be added to existing singlefamily
residential communities. There was a
concern … over how existing single-family
homes were being impacted by new, adjacent
denser developments. …
“The tiering policy required…a transition zone
along the southern portion of Phase 10 equal to
‘the depth of the first block of single-family lots’
within the northern portion of Phase 1. The
section requires that development in the first tier
of Phase 10 be limited to construction ‘of
comparable density and compatible dwelling unit
types.’ The court finds that the appropriate
measure is 225 feet, using the shortest average
depth method of computation.
“No transition zone was established for Phase
10. The buildings along the first tier of Phase 10
are multi-family, multi-story, and have balconies.
The southern tier of Phase 10 has a density of
6.6 [UPA]. The overall density of Phase 10 is
6.5 [UPA]. There is no meaningful difference
in density across the entire western portion of
Phase 10. The northern tier of Phase 1, on the
other hand, is comprised entirely of single-family
homes on 0.75 acre to 1.2 acre lots, with a
density of 0.94 [UPA].
13“There was no first tier transition zone
established for Phase 10 as mandated by section
4-5(A)(2)(b). That section is not the only
provision of the Comprehensive Plan that
mandated compatible structures within the first
tier of Phase 10. Section 4-4(M)(1)(e)(2)
provided:
… Where single family structures comprise
the dominant structure type within [residential
estate densities (RE-0.5A)], new development
on undeveloped abutting lands shall be
13At this point in the Final Judgment, the court went
on to show in a comparative table that the change in
density between the two tiers represented a 560%
difference, the change in population a 492% difference,
and the number of units a 418% difference.
(11)
required to include compatible structure types of
lands immediately adjacent to existing family
development.
… Phase 1 is designated RE-0.5A
…
“It is impossible … to examine the photographs
of the homes in the northern tier of Phase 1, and
the apartment buildings in the southern tier of
Phase 10, and find that they are either
‘compatible dwelling unit types’ or ‘compatible
structure types.’ The only residential structure
that could be less compatible with the northern
tier of Phase 1, would be a multi-story
condominium building. There is no compatibility
between the structures in the southern tier of
Phase 10 and the northern tier of Phase 1.
Further, an examination of the density of
development in the two tiers at issue, precludes
this court from finding that they are in any way
comparable.
…
“[B]uffering does not grant relief to the
[developer] under section 4-4(I)(5). That
section deals with buffering between
‘incompatible land uses.’ The more specific
Tiering Policy mandates compatibility. More
importantly, even to the extent that the
Comprehensive Plan might, in some instances,
provide a builder with the ability to buffer
changes in density, intensity or uses, the
language of sections 4-4(M)(1)(e)(2) and 4-
5(A)(2)(b) simply do not permit the type of
development that is under construction in Phase
10.”
…
“Based on the foregoing, the Court finds that
the Development Order is inconsistent with the
Comprehensive Plan. It is not compatible with,
nor does it further the objective, policies, land
uses, densities and intensities in the
Comprehensive Plan. § 163.3194(3)(a).” [e.o.]
We have carefully reviewed the record of the
trial and the evidence presented. It is apparent
that there is substantial competent evidence to
support these findings. Developer argues that the
court erred in its interpretation of the “tiering
policy,” in deeming it a mandatory requirement
rather than a discretionary guide. We conclude
that the trial court’s construction is consistent with
the plain meaning of the text of the
Comprehensive Plan. See Comprehensive Plan,
§ 4-5(A)(2)(b) (“a density transition zone of
comparable density and compatible dwelling unit
types shall be established in the new project for a
depth from the shared property line that is
equivalent to the depth of the first tier of the
adjoining development’s lower density (i.e. the
depth of the first block of single-family lots).”).
Moreover, given the evidence as to Martin
County’s adoption of the tiering policy, the record
clearly supports the finding that the policy was
intended to be applied in all instances of projects
abutting single-family residential areas. We
therefore affirm the finding of inconsistency and
proceed to explain our decision on the remedy.
II. Remedy of Demolition
Developer challenges what it terms the
“enormity and extremity of the injunctive remedy
imposed by the trial court.” It argues that the trial
court’s order requiring the demolition of 5 multifamily
residential buildings is the most radical
remedy ever mandated by a Florida court because
of an inconsistency with a Comprehensive Plan.
Specifically, the contention is that the trial judge
failed to balance the equities between the parties
and thus ignored the evidence of a $3.3 million
dollar loss the developer will suffer from the
demolition of the buildings. The court failed to
consider alternative remedies in damages, it
argues, that would have adequately remedied any
harm resulting from the construction of structures
inconsistent with the Comprehensive Plan.
Developer maintains that the trial court
erroneously failed to give meaningful consideration
to the traditional elements for the imposition of
injunctive relief. It contends that the trial court
proceeded on an erroneous conclusion that where
an injunc tion is sought on the basis of a statutory
violation, no proof is required as to the traditional
(12)
elements for an injunction.
Traditionally, as the trial judge noted, it is true
that injunctions are usually denied where the party
seeking such relief fails to demonstrate a clear
legal right, a particular harm for which there is no
adequate remedy at law, and that considerations
of the public interest would support the injunction.
See, e.g., St Lucie County v. St. Lucie Village,
603 So. 2d 1289, 1292 (Fla. 4th DCA 1992).
These are, of course, the necessary ingredients for
equitable relief when we labor in the interplay of
common law and equity, where ordinary legal
remedies are unavailing.
Nonetheless, as between the State legislature
and the several counties, the Legislature is the
dominant creator of public duties and citizen
rights.
14 Recognizing that the Legislature has thesole power to create such public duties and citizen
rights, it logically follows that the Legislature is
necessarily endowed with the authority to spec ify
precisely what remedies shall be used by judges to
enforce a statutory duty—regardless of whether
in general usage such a remedy usually requires
additional factors before it is traditionally
employed.
When the Legislature creates a public duty and
a corresponding right in its citizens to enforce the
duty it has created, and provides explicitly that the
remedy of vindication shall be an injunction, the
Legislature has not thereby encroached on judicial
powers, as the courts held in Harvey v.
Wittenberg, 384 So. 2d 940 (Fla. 3rd DCA 1980),
and Times Publishing Co. v. Williams, 222 So. 2d
470 (Fla. 2d DCA 1969). The Times Publishing
court explained its theory of encroachment thus:
“Injunctive relief is an extraordinary remedy
which issues only when justice requires and
there is not adequate remedy at law, and when
there is a real and imminent danger of
irreparable injury. Statutory authority for such
writs, as in the act before us, are not
uncommon; but it must be remembered that
such writs are in the first instance judicial writs.
If such statutes purport to give the circuit courts
injunctive power they are ineffectual, since
those courts are otherwise vested with such
powers under the constitution, § 6(3) Art. V
Constitution of Florida; and if they purport to
dictate to such courts when, how or under what
conditions injunctions should issue they would
constitute an unlawful legislative infringement on
a judicial function.” [e.s.]
222 So. 2d at 476. Times Publishing and Harvey
both held that the Legislature is limited to
specifying certain harms as irreparable, but the
court alone has the discretion to determine
whether the injunction should otherwise issue. We
disagree with this analysis.
We think that is too wooden a construction of
legislative powers where a statute is concededly
valid. In our view when the Legislature provides
for an injunction in these circumstances, it has
deliberately made the new public duty and its
corresponding right of enforcement an integrated
statutory prescription. By specifying that the
public interest requires that a certain duty be
vindicated in the courts and not primarily within
other branches of government, the Legislature is
well within its powers. Surely the Legislature’s
primary role in defining public policy under the
constitution is broad enough to enable it to specify
a legal remedy in an enactment, regardless of
whether the traditional judicial restrictions on that
remedy in other, non-statutory contexts would limit
its usage. As the author of the primary duty, the
Legislature alone shapes the form of its
effectuating mechanism.
In section 163.3215, we think the Legislature
has constructed such a statute. The statute leads
off with a declaration that:
“Any aggrieved or adversely affec ted party
may maintain an action for injunctive or other
14
See Art. VIII, § 1(f) and (g), Fla. Const. (whethercharter or non-charter government, Counties are
granted power to enact only ordinances that are “not
inconsistent with general law”).
(13)
relief against any local government to prevent
such local government from taking any action on
a development order, as defined in s. 163.3164,
which materially alters the use or density or
intensity of use on a particular piece of property
that is not consistent with the comprehensive plan
adopted under this part.”
From the plain and obvious meaning of this text
we discern only two elements to the granting of an
injunction against the enforcement of a
development order: (a) the party is affected or
aggrieved by (b) an approved project that is
inconsistent with the Comprehensive Plan. In
short, the existence of an affected neighbor is all
that is necessary for the issuance of an injunction
against a proposed land use that is inconsistent
with the Comprehensive Plan.
We note that the statute does not say that the
affected/aggrieved party bringing the action
“creates a presumption of irreparable injury” by
showing an inconsistency with the Plan. See, e.g.,
§ 542.335(1)(j), Fla. Stat. (2000) (“The violation of
an enforceable restrictive covenant creates a
presumption of irreparable injury to the person
seeking enforcement of a restrictive covenant.”).
When the Legislature wants to make a lesser
intrusion on traditional equitable jurisdiction, it
obviously knows how to do so. Here the statutory
text makes the injunction the first and preferred
remedy to alleviate the affects of in inconsistent
land use. Hence, we read the statute to make the
injunction the presumed remedy where the
conditions prescribed are shown.
15We disagree with the developer’s contention
that this statute was meant to create mere
discretion in the court to issue an injunction. If
injunctive relief is the specified, primary remedy to
correct a violation of a public duty and to vindicate
the right of a person affected by the violation of
that duty, it can properly be deemed a rule that the
Legislature has created, not a grant of discretion.
Here the Legislature has devised an entire
statutory scheme to insure that all counties have a
Comprehensive Plan for the development of land
within their respective jurisdictions. The scheme
creates mandatory duties to have a plan,
mandatory duties to have the plan approved by the
state, and once approved mandatory duties to limit
all developments so that they are consistent with
the plan’s requirements. At the end of all these
mandatory duties—all these shalls—comes a new
relaxation of the requirements on standing for
citizen suits to enforce comprehensive land use
15We reject developer’s argument that demolition is
improper simply because Shidel failed to seek a
temporary injunction against any construction while
the case proceeded in court on the consistency issue.
In the first place, when the action was filed the trial
court originally thought its role limited to a record
review of the proceedings before the Martin County
Commission and concluded that no error had been
shown. Having decided there was no error in the
limited review it thought applicable, the trial court was
hardly likely to grant a temporary injunction while the
case was on appeal.
Even more important, however, we find nothing in the
text of the relevant statutes making such a request for
a temporary injunction a precondition to effective final
relief after a trial de novo when the court finds that the
permitted use is inconsistent with the Comprehensive
Plan. We note from other statutes that when the
Legislature means to place restrictions on third party
challenges to agency decisions granting permits, it
says so in specific text. Compare § 403.412(2)(c), Fla.
Stat. (2000), with § 163.3215(4), Fla. Stat. (2000), as to
preconditions for suit; see also § 163.3215(6), Fla. Stat.
(2000) (“The signature of an attorney or party
constitutes a certificate that he or she has read the
pleading, motion, or other paper and that, to the best of
his or her knowledge, information, and belief formed
after reasonable inquiry, it is not interposed for any
improper purpose, such as to harass or to cause
unnecessary delay or for economic advantage,
competitive reasons or frivolous purposes or needless
increase in the cost of litigation. If a pleading, motion,
or other paper is signed in violation of these
requirements, the court, upon motion or its own
initiative, shall impose upon the person who signed it,
a represented party, or both, an appropriate sanction,
which may include an order to pay to the other party or
parties the amount of reasonable expenses incurred
because of the filing of the pleading, motion, or other
paper, including a reasonable attorney's fee.”).
(14)
plans and providing for the issuance of injunctions
when an inconsistency affects another land
owner. Judicial construction of that sole remedy
as discretionary strikes us as remarkably
inconsistent with not only the text of the statute
itself but also with the purpose of the entire
legislative scheme.
Developer lays great stress on the size of the
monetary loss that it claims it will suffer from
demolition, as opposed to the much smaller
diminution in value that the affected property
owner bringing this action may have suffered. It
contends that a $3.3 million loss far outweighs the
evidence of diminution in the value of Shidel’s
property, less than $26,000. Its primary contention
here is that the trial judge erred in failing to weigh
these equities in its favor and deny any remedy of
demolition. Instead, as developer sees it, the court
should have awarded money damages to eliminate
the objector’s diminution in value. Developer also
argued that instead of demolition it should be
allowed to build environmental barriers, green
areas of trees and shrubbery, between the
apartment buildings and the adjoining area of
single family homes.
Developer emphasizes that we deal here with an
expensive development: “a high quality, upscale
project;” “forty units of high-quality garden
apartments;” “five upscale multi-family dwellings,
housing 40 garden apartments, at a value of
approximately $3 million.” Developer concedes
that there is evidence showing that plaintiff
Shidel’s property is diminished by $26,000. It also
concedes that the total diminution for all the homes
bordering its project is just under $300,000.
Developer contends, however, that the real
countervailing harm to all these affected property
owners in the vicinity is not any diminution in the
value of their homes, but instead is merely
“knowing that there is an upscale apartment
building approximately a football field away,
partially visible through some trees behind the
house.”
Section 163.3215 says nothing about weighing
these specific equities before granting an
injunction. If the Legislature had intended that
injunctive enforcement of comprehensive plans in
the courts be limited to cases where such
imbalances of equities were not present, we
assume that it would have said so. As important,
such balancing if applied generally would lead to
substantial non-compliance with comprehensive
plans. We doubt that there will be many instances
where the cost of the newly allowed construction
will be less than any diminution resulting from an
inconsistency. Entire projects of the kind
permitted here will frequently far exceed the
monetary harms caused to individual neighbors
affected by the inconsistency. In other words, if
balancing the equities—that is, weighing the loss
suffered by the developer against the diminution in
value of the objecting party—were required
before demolition could be ordered, then
demolition will never be ordered.
Moreover it is an argument that would allow
those with financial resources to buy their way out
of compliance with comprehensive plans. In all
cases where the proposed use is for multiple acres
and multiple buildings, the expenditures will be
great. The greater will be its cost, and so will be
a resulting loss from an after-the-fact demolition
order. The more costly and elaborate the project,
the greater will be the “imbalance in the equities.”
The more a developer is able to gild an
inconsistency with nature’s ornaments—trees,
plants, flowers and their symbiotic fauna—the
more certain under this argument will be the result
that no court will enjoin an inconsistency and
require its removal if already built.
In this case the alleged inequity could have been
entirely avoided if developer had simply awaited
the exhaustion of all legal remedies before
undertaking construction. It is therefore difficult
to perceive from the record any great inequity in
requiring demolition. Shidel let the developer
know when it was just beginning construction of
the first building that she would seek demolition if
(15)
the court found the project inconsistent. When
developer decided to proceed with construction in
spite of the absence of a final decision as to the
merits of the challenge under section 163.3215, the
developer was quite able to foresee that it might
lose the action in court. It could not have had a
reasonable expectation that its right to build what
it had proposed was finally settled. It may have
thought the decision to build before the
consistency question was settled in court a
reasonable “business decision,” but that hardly
makes it inequitable to enforce the rule as written.
It also seems quite inappropriate, if balancing of
equities were truly required by this statute, to
focus on the relatively small financial impacts
suffered by those adjoining an inconsistent land
use. The real countervailing equity to any
monetary loss of the developer is in the flouting of
the legal requirements of the Comprehensive Plan.
Every citizen in the community is intangibly
harmed by a failure to comply with the
Comprehensive Plan, even those whose properties
may not have been directly diminished in value.
We claim to be a society of laws, not of
individual eccentricities in attempting to evade the
rule of law. A society of law must respect law,
not its evasion. If the rule of law requires land
uses to meet specific standards, then allowing
those who develop land to escape its requirements
by spending a project out of compliance would
make the standards of growth management of
little real consequence. It would allow developers
such as this one to build in defiance of the limits
and then escape compliance by making the cost of
correction too high. That would render section
163.3215 meaningless and ineffectual.
In this regard we are drawn to the views
expressed in Welton v. 40 Oak Street Building.
Corp., 70 F.2d 377 (7th Cir. 1934), a case of
strikingly analogous facts. There the developer
applied for a permit to erect a building, and
proceeded to build while its neighbor objected to
the edifice and sought to show that the building
plans did not comply with the zoning ordinances.
When the agency approved the building he sought
relief in the courts, finally being victorious in the
state supreme court. Ownership of the building
meanwhile passed to a federal receiver, and so the
objecting neighbor sought to enforce his remedy
by injunctive relief in the federal court. The trial
judge denied an injunction. On appeal the Court of
Appeals disagreed and ordered a mandatory
injunction to “rebuild” the edifice in compliance
with the zoning law, explaining:
“We have earnestly endeavored to place
ourselves in a position to fully appreciate
appellees’ argument to the effect that
enforcement of a right which arises out of an
effort to give light and air to metropolitan areas
is an equity that is outweighed by the dollars
advanced by builders of twenty story buildings in
defiance of zoning ordinances. We have also
endeavored to obtain appellees’ viewpoint when
they propose a money judgment to one who
suffers small financial loss as satisfaction for
violation of important ordinances enacted for the
benefit of the public. In the fight for better living
conditions in large cities, in the contest for more
light and air, more health and comfort, the scales
are not well balanced if dividends to the
individuals outweigh health and happiness to the
community. Financial relief to appellants is not
the only factor in weighing equities. There is
involved that immeasurable but nevertheless
vital element of respect for, and compliance
with, the health ordinance of the city. The
surest way to stop the erection of high buildings
in defiance of zoning ordinances is to remove all
possibility of gain to those who build illegally.
Prevention will never be accomplished by
compromise after the building is erected, or
through payment of a small money judgment to
some individual whose financial loss is an
inconsequential item.”
70 F.2d at 382-83. We agree with the Seventh
Circuit that respect for law, in this case the
Comprehensive Plan, trumps any “inequity” of
financial loss arising from demolition.
(16)
Our understanding of section 163.3215 is thus
different from equity’s traditional use of its
remedies. If, as we have shown, an injunction is
the statutory remedy to insure consistency of
development of property within the county, it does
not seem to us that the kind of balancing
advocated here would further that goal. In fact it
would very likely lead to even more inconsistent
development, particularly as to the kind of large
scale projec t involved here with multiple buildings
for multiple families. As we see it, the purpose of
this statute is precisely against this kind of
thinking. A clear rule is far more likely to erase
the kind of legal unpredictability lamented by
developer and amici.
The statute says that an affected or aggrieved
party may bring an action to enjoin an inconsistent
development allowed by the County under its
Comprehensive Plan. The statutory rule is that if
you build it, and in court it later proves
inconsistent, it will have to come down. The
court’s injunction enforces the statutory scheme
as written. The County has been ordered to
comply with its own Comprehensive Plan and
restrained from allowing inconsistent development;
and the developer has been found to have built an
inconsistent land use and has been ordered to
remove it. The rule of law has prevailed.
We therefore affirm the final judgment of the
trial court in all respects.
GUNTHER and GROSS, JJ., concur.
NOT FINAL UNTIL DISPOSITION OF ANY TIMELY
FILED MOTION FOR REHEARING.
TDR Case Studies Updates
Beyond Takings and Givings contains case studies of 142 TDR programs in 134 communities around the nation. Since that book went to press in January 2003, TDR programs have been adopted, discovered or updated in the following communities. Rick Pruetz, who prepares these profiles, runs a consulting practice specializing in TDR workshops, studies and ordinances. Please contact him at arje@attglobal.net with corrections, updates or information on additional programs.
Chesterfield Township, Burlington County, New Jersey
Los Ranchos de Albuquerque, New Mexico
Lumberton Township, Burlington County, New Jersey
|
Approved
Appraiser List Application |
|
Aquatic Plant Removal Permit Application (pdf 35k, requires Acrobat Reader) |
|
Application for processing and collecting aquatic plants for Importation, Transportation, Non-Nursery Cultivation, Possession, and Collection (pdf 95k, requires Acrobat Reader) Rules |
|
Application for removing aquatic plants (pdf 35k, requires Acrobat Reader) Rules |
|
DEP 63-030 (16) (doc) Application for Recordable Document for Lands Filled Prior to July 1, 1975 Pursuant to Chapter 253.12(9) & (10), Florida Statutes |
|
Affidavit Example for Lands Filled Prior to July 1, 1975-"75 Certificate" |
|
DEP 63-031 (16) (doc) Application for Disclaimers to Confirm Title of Formerly Sovereignty Lands Pursuant to Chapter 253.129, Florida Statutes |
|
DEP 63-032 (16) (doc) Application for Quitclaim Deed to Clear Title of Formerly Sovereignty Lands Pursuant to Chapter 253.12(6), Florida Statutes |
|
DEP 62-068 (16) (doc) Application to Purchase Lands Lost Due to Artificial Erosion or Artificial Erosion and Avulsion |
|
DEP 62-069 (16) (doc) Application for Disclaimer for Lands Lost Due to Avulsion |
SMATHERS LIBRARIES |
---Web Resources for Urban Planning |
![]() |
Introduction
This guide provides links to websites of high quality of likely interest to researchers in architecture. Recommendations for additions or revisions to this guide are welcomed. This guide is one of three which make up the Architecture Subject Guide. The other guides deal with Reference Collection sources and Databases.-
|
Planning
Subject Guide | AFA Library | UF
Libraries | UF
Julie Quick (202) 720-4632
Mary Cressel (202) 690-0547
VENEMAN ANNOUNCES RELEASE OF $1.6 BILLION FOR VOLUNTARY CONSERVATION PROGRAMS ON WORKING LANDS
WASHINGTON, Oct. 22, 2004—Agriculture Secretary Ann M. Veneman today announced the release of $1.6 billion in fiscal year 2005 funding for conservation programs on working lands, which, by knowing the initial mandatory program funding and technical assistance levels well before the next planting season begins, will help producers connect their business decisions to protecting water, air, soil and wildlife.
"This is one of the largest investments in conservation on private lands in our nation’s history," Veneman said. "In making the announcement today, we are responding to agricultural producers who want greater certainty and predictability in their decisions regarding environmental stewardship before planting season begins."
Veneman said that these program funds were being provided much earlier than in the past.
"Releasing the funds earlier in the year gives farmers and ranchers more time to make sound decisions regarding conservation practices," said Veneman. "This announcement will make conservations programs fully operational in every state and give producers the information they need to develop more effective conservation plans."
Veneman added that this effort is another example of the Bush Administration’s commitment to providing the tools and resources that will help agriculture producers remain the best stewards of the land. For example, on Earth Day 2004, President Bush highlighted the progress made by USDA in restoring America’s wetlands and announced an aggressive national goal to increase overall wetland acres and quality by restoring, improving and protecting at least 3 million wetland acres over the next five years. To help meet this goal, the President called on Congress to pass his FY 2005 Budget request, which includes $4.4 billion for conservation programs. By surpassing the decade-old "no-net-loss" policy, the President sent a message that we can continue the fight against soil erosion, improve the quality of our water and air and enhance wildlife habitat across America’s productive agricultural landscape.
In August, the President announced an expansion of the Conservation Reserve Program (CRP). As part of this announcement, the President unveiled CRP initiatives to create 250,000 acres of habitat for the northern bobwhite quail and to restore 250,000 acres of wetlands and playa lakes located outside the 100-year floodplain.
-more-
-2-
In September, the President issued an Executive Order, Facilitation of Cooperative Conservation, which promotes cooperative conservation. The Executive Order emphasized appropriate local participation in Federal decision-making, in accordance with respective agency missions, policies and regulations. Cooperative conservation will enhance the enjoyment of natural resources through greater protection of the environment by involving collaborative activity among Federal, State, local and tribal governments, private for-profit and nonprofit institutions, other nongovernmental entities and individuals.
To help implement these initiatives, the Administration is announcing the initial conservation funding allocation today to allow USDA’s Natural Resources Conservation Service (NRCS) conservationists to work with farmers and ranchers nationwide to improve soil, water, air and at-risk habitat on privately-owned working lands in several programs.
Fiscal year 2005 allocations include $1.310 billion in financial assistance and $306 million for technical assistance for NRCS voluntary conservation programs and other activities. Veneman said that States will receive additional money after Congress makes discretionary funding decisions.
With financial and technical assistance from NRCS, farmers, ranchers and other landowners will continue to address resource concerns on agricultural working lands, promote environmental quality, address challenges in water quality and quantity, protect prime farmland and grazing lands and protect valuable wetlands ecosystems and wildlife habitat.
Key conservation programs and allocations include:
Environmental Quality Incentives Program (EQIP): $793,590,395. EQIP assists farmers and ranchers to improve soil, air and water quality and other related resources on private working lands.
Ground and Surface Water Conservation (GSWC): $62,874,481. GSWC assists farmers and ranchers to conserve our nation’s ground and surface water resources. The funding will result in improving agricultural water use efficiency and result in a net savings to ground and surface water reserves.
Klamath Basin: $9,734,200. These funds will help farmers and ranchers to enhance water quality, reduce water usage by increasing irrigation efficiencies, and improve habitat for affected fish and wildlife in the Klamath Basin.
Wetlands Reserve Program (WRP): $244,533,800. WRP is a voluntary program that helps landowners restore, enhance and protect wetlands through permanent easements, 30-year easements and restoration cost-share agreements. The program works to maximize wildlife habitat and wetland functions and values.
-more-
-3-
Farm and Ranchland Protection Program (FRPP): $66,574,678. FRPP is a voluntary program that provides matching funds to state and local governments and non-governmental organizations to purchase conservation easements on farm and ranch land. Since 1996, FRPP, in partnership with state and local governments and nongovernmental organizations, has protected over 440,000 acres.
Grassland Reserve Program (GRP): $40,832,400. GRP is a voluntary program designed to protect and restore grasslands, biodiversity, wildlife habitat and reduce soil erosion while sustaining viable working ranches. In 2005, GRP will utilize over $2 million to benefit the Greater Sage Grouse in key western states and protect precious Tall Grass habitat in Kansas.
Wildlife Habitat Incentives Program (WHIP): $21,935,051. WHIP offers technical and financial assistance through long-term agreements to create, restore and enhance wildlife habitat for upland wildlife, wetland wildlife, threatened, endangered or at-risk species and fisheries as well as other types of wildlife.
Agricultural Management Assistance (AMA): $12,997,456. AMA is available in 15 states where participation in the Federal Crop Insurance Program has been historically low: Connecticut, Delaware, Maine, Maryland, Massachusetts, Nevada, New Hampshire, New Jersey, New York, Pennsylvania, Rhode Island, Utah, Vermont, West Virginia and Wyoming. It helps farmers and ranchers voluntarily address natural resource concerns by incorporating conservation into farming operations while managing financial risk.
Conservation Reserve Program (CRP): $56,599,700 in technical assistance. CRP, administered by the Farm Service Agency, encourages farmers and ranchers to voluntarily establish conservation practices to protect environmentally sensitive land, provide food and habitat for wildlife and protect ground and surface water from runoff and sedimentation. Since the inception of CRP in 1986, this program has helped reduce soil erosion by more than 40 percent and restored 1.8 million acres of critical wetland acreage.
In addition, the allocation includes dollars for the Conservation Security Program (CSP). It includes $32,386,009 for active contracts and $162,024,991 for 2005 sign-up. State allocations for sign-up will be made at a later date. CSP recognizes those producers who are excellent stewards of the land and are willing to do even more by supporting ongoing conservation stewardship of agricultural working lands. In 2004, CSP was offered in 18 watersheds. In 2005 it is expected to be available in watersheds in all 50 states and a renewable energy component will be introduced that rewards farmers and ranchers for converting to renewable energy fuels such as soy bio-diesel and ethanol, for recycling 100 percent of on-farm lubricants, and for implementing energy production, including wind, solar, geothermal, and methane production.
A list of allocation totals by states is attached. Additional information on conservation programs is available at http://www.nrcs.usda.gov/programs. Landowners who want specific information regarding program participation should contact their local USDA Service Center or NRCS office, locate at http://offices.usda.gov or in the telephone book under Federal Government, U.S. Department of Agriculture.
#
FY 2005 Conservation Funding Allocation Totals by State:
|
FLORIDA |
$39,180,466 |
* State allocations for CSP sign-up will be made at a later date.
S
TUDYA
NALYSIS OF AGRICULTURAL LANDR
ETENTION STRATEGIEST
ASK 2.B.S
UBMITTED BY:R
OBERT H. FREILICH, AICP, LL.M., J.D.T
YSON SMITH, AICP, J.D.E
LISA PASTER, M. SC.F
REILICH, LEITNER & CARLISLEWITH SUPPORT FROM
T
ISCHLER & ASSOCIATESAND
U
NIVERSITY OF FLORIDAMiami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
1
T
ABLE OF CONTENTSI. Introduction..................................................................................................................2
A. Task 2: Agricultural and Rural Area Retention and Promotion Strategies .............2
B. Task 2(b): Analysis of Agricultural Land Retention Strategies ..............................2
C.
The Goal: Protection of Agricultural Land Values and the Essential Character ofthe Study Area .................................................................................................................3
II. Overview......................................................................................................................4
A. Land Use Growth Patterns .......................................................................................4
B. Agricultural Land .....................................................................................................6
C. Economic Impact of Agricultural Land ...................................................................7
D. Growth Management Challenges ............................................................................7
III. Agricultural and Rural Land Policies and Implementation Techniques..................8
A. Agricultural Zoning .................................................................................................8
1. Area Based Zoning ..............................................................................................9
2. Large Lot Zoning .................................................................................................9
3. Cluster Zoning ...................................................................................................10
4. Buffering............................................................................................................12
5. Overall Benefits and Drawbacks of Agricultural Zoning..................................14
B. Non-Zoning Techniques ........................................................................................15
1. Right-to-farm Laws ...........................................................................................15
2. Agricultural Districting......................................................................................17
3. Land Evaluation Systems ..................................................................................18
C. Land Acquisition Programs ...................................................................................20
1. Conservation Easements ....................................................................................20
2. Purchase of Development Rights.......................................................................20
3. Land Banking.....................................................................................................22
4. Transfer of Development Rights .......................................................................23
5. Florida Rural and Family Lands Protection Act ................................................26
D. Taxation Programs .................................................................................................27
1. Differential Assessment .....................................................................................27
2. Circuit Breaker Tax Relief Credits ....................................................................28
3. Real Estate Transfer Taxes ................................................................................29
E. Funding Programs..................................................................................................30
1. Impact Fees ........................................................................................................30
2. Environmental Mitigation Fees .........................................................................31
3. Federal Programs ...............................................................................................31
F. Regulatory Techniques ..........................................................................................32
1. Growth Tiers ......................................................................................................32
2. Concurrency Programs ......................................................................................33
3. Urban Service Boundaries .................................................................................34
IV. Economics and the Law.........................................................................................35
A. Economic Value of Land .......................................................................................35
B. Legal Framework ...................................................................................................35
1. Takings ..............................................................................................................36
2. Impact Fees/ Mitigation Fees.............................................................................37
3. Due Process .......................................................................................................38
V. Miami-Dade County – Value Preservation Principle ................................................38
VI. Conclusion.............................................................................................................39
Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
2
The authors have prepared this analysis in completion of Task 2(b)
of the Scope of Services, “Agricultural and Rural Area Retention and
Promotion Strategies.” It is not the goal of this analysis to propose one
solution or another as appropriate to the Study Area, or to suggest one
policy approach over any other. Rather, this analysis is intended to set
forth alternative techniques that the CAC may recommend and the County
may adopt in pursuit of its overarching land use objectives in the Study
Area.
Tyson Smith, of the law firm, Freilich, Leitner & Carlisle, and coauthor
of this analysis, attended the August 21, 2002 meeting of the CAC,
presented the findings made herein, and received the initial input of the
Committee. This Report reflects the comments received at that meeting,
as well as additional comments received from other members of the
Consultant Team, staff, and the TAC.
The Task 2(c) report, “Analysis of Rural Land Uses,” presents a
case analysis of five different communities around the country that have
incorporated a number of the preservation techniques discussed in this
report. In Task 2(c) we focused on the “value preservation” mechanisms –
e.g.
, purchase or transfer of development rights – applied by thecommunities to achieve successful agriculture and rural area programs.
Value preservation mechanisms make most programs successful, due
mainly to the fact that they protect both the agricultural and the
preservation interests of the community. This Report provides an
overview of zoning and incentive driven programs that may, in the final
analysis, constitute the ultimate recommendation of the Consultant Team.
I. I
NTRODUCTIONA. Task 2: Agricultural and Rural Area Retention and Promotion Strategies
Task 2 of the Scope of Services focuses on a range of agriculture and rural area
retention, promotion, and economic development strategies. Task 2(a) presents and
analyzes information on various economic development issues; Task 2(c) introduces
related programs used in similarly situated rural areas of the country; and, finally, Task
2(d) will include a recommended approach for addressing the specific needs of Miami-
Dade County.
B. Task 2(b): Analysis of Agricultural Land Retention Strategies
Objective:
Collect, analyze and present information regardingagricultural land retention strategies and implementing programs used in
areas facing similar urbanization pressures, as well as development rights
programs, land swaps, or any other means to ensure that landowner
equity is maintained, with emphasis on the success of such programs, their
ability to solve shortcomings and their applicability to Miami-Dade
County without negative effects on agricultural competitiveness.
Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
3
The goal of Task 2(b) is to present and analyze information regarding agricultural
and rural land use strategies and programs used in areas facing development pressures
similar to those in existence or anticipated in the Study Area. Section II of this Report
provides a general overview of the range of issues that underlie the overall analysis being
undertaken by the Consultant Team (the “Team”). Section III sets out numerous
agriculture and rural land use techniques that are available to the County in pursuit of its
overall rural policies. Section IV assesses the applicability and legality of various land
use policies and preservation techniques within the Study Area. And, finally, Section V
sets forth the proposed framework for analyzing or determining a policy approach that
will achieve the dual goal of this analysis: the protection of land values and the
preservation of agriculture and rural open space within the Study Area.
C.
The Goal: Protection of Agricultural Land Values and the EssentialCharacter of the Study Area
Preserving the value of agricultural land is imperative to ensuring long term
preservation of farming, open space, and managed growth. Farmers, growers, and
ranchers own 80 percent of the private land in Florida; land that provides wide-open
views of forestlands, green groves, and pastureland.
1 However, many of these large-scaleproperty owners are selling their land because encroaching urban uses have deemed
agricultural uses economically non-viable. When land value is diminished, future
economic development is limited. During times of economic hardship, the agricultural
landowner may have to rely on the underlying value of his or her land to make financing
arrangements to cover the cost of operations. If land values are significantly reduced, so
are refinancing opportunities, leaving the farmer in difficult financial straits. Preserving
land values is beneficial not only for the land owner, but also for the entire community;
while the farmer continues to farm, the community benefits from open space and
managed growth.
This paper concludes with a proposal for analyzing and developing a “preferred
development scenario” for achieving the long-term land use goals for the Study Area.
The authors propose that this analysis – this weighing of alternative techniques and
approaches – be conducted in light of the actual economic reality that landowners in the
Study Area will face over a twenty-year period. Simply put, that decision will be
whether to retain existing holdings in their current use, or a significant portion thereof; or
to develop those holdings at some undetermined urban or suburban density.
The framework of this analysis presumes, first, that a combination of
agriculture/rural open space preservation and reasonable development will characterize
the Study Area over the next twenty years. Second, it further presumes that this
combination of land use intensities will be defined by adopted County policies, which in
turn, may be based significantly on the recommendations of the Team and the Citizens’
Advisory Committee (the “CAC”). Third, this analysis contemplates an ultimate
“preferred development scenario” – to be determined and articulated under Task 2(d) –
that preserves both property rights and rural character, but neither at the expense of the
1
Florida Farm Bureau, Growth Management, available athttp://www.fb.com/flfb/issues/2001/Growmgt.htm
(August 2, 2002).Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
4
other. The authors believe that reasonable policies can be drafted and implemented,
which will advance both property rights and the rural policies of the County, while
protecting land values throughout the Study Area. The Alternatives Analysis set forth at
Section V proposes a framework for arriving at that ultimate recommendation.
II. O
VERVIEWA. Land Use Growth Patterns
Florida is one of the fastest growing states in the nation, and rural lands still
constitute a majority of land within the state.
2 While rural populations accounted for only7 percent of the state’s population in 1997, the growth rate of rural Florida has been
outpacing the national average.
3 From 1990 to 2000, the population of Miami-DadeCounty grew 12.3 percent.
4Historically, Miami-Dade County’s land use patterns have reflected patterns
across America: loss of agricultural land to urban development; rising land prices on the
urban fringe; and urban sprawl. Since World War II the greatest proportion of growth
has taken place in the urban-rural fringes of major metropolitan centers. This type of
growth has led to the depletion and deprivation of important environmental resources,
including the loss of unique agricultural lands.
5 As urban growth spreads into the ruraland semi-rural areas of Miami- Dade County, the character unique to the rural community
is threatened.
6In 1985, the Florida Legislature passed into law the Local Government
Comprehensive Planning and Land Development Regulations Act (the “Growth
Management Act”). The Growth Management Act set up a public hearing and permitting
process for regional planned growth that protects important public natural resources
including rivers, lakes, springs, state parks, and rare wildlife species. The Growth
Management Act mandates comprehensive planning for local governments and vested the
Florida Department of Community Affairs (DCA) with an oversight role. From local to
regional to statewide comprehensive plans, DCA provides checks and balances to growth
and development, ensuring that developers and existing taxpayers alike foot some of the
costs associated with growth such as new schools, roads, new utilities (drinking water,
sewage treatment, electric, telephone), municipal services (fire, police, ambulance), and
additional parks and recreation areas.
7The County’s Comprehensive Development Master Plan and its accompanying
Land Use Planning (LUP) map guide land use patterns in Miami-Dade County. The
Urban Development Boundary (UDB) is one of the major components of the land use
strategy in Miami-Dade County as it demarcates where urban development ends and rural
2
Florida Chapter of the American Planning Association & 1000 Friends of Florida, Rural Florida:Opportunities for the Future
, 3 (February 2002).3
Id.4
South Florida Regional Planning Council, Table: Southeast Florida Components Of Population Changeavailable at
http://www.sfrpc.com/region/sfcmigc1.htm (August 1, 2002).5
Robert H. Freilich & Linda Kirts Davis, Saving the Land: The Utilization of Modern Techniques ofGrowth Management to Preserve Rural and Agricultural America
, 13 URB. LAW. 27, 29 (1981).6
See Fred Heyer, Perserving Rural Character, APA Planning Advisory Service Report no. 429, 1 (1990).7
See generally Fla. Stat. §163 (2002).Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
5
development begins.
8 The purpose of the UDB is to ensure that development only occursin areas where infrastructure is available and to ensure vital natural resources are
protected outside the boundary. Development within the UDB will be approved through
the year 2005 provided that adequate services and public facilities are available.
9 TheLUP also has a year 2015 Urban Expansion Area (UEA) boundary. The UEA is
comprised of that area located between the 2005 UDB and the 2015 UEA boundary. It is
the area where current projections indicate that further urban development beyond the
2005 UDB boundary is likely to occur between 2005 and 2015. Until this area is brought
into the UDB area through plan and review amendment processes, parcels are allowed to
be used for agricultural and open space use.
10Any person or organization, including the federal government, the State of
Florida, Miami-Dade County, any municipality in Miami-Dade County and any of their
agencies, authorities and departments may request amendment of the UDB and UEA.
The County Commission must review the Comprehensive Development Master Plan
every two years and any proposed amendment to the UDB may only be submitted in odd
years during a certain period in April.
11 In considering amendments to the UDB theCommission must meet all the requirements of the Growth Management Act and will
consider issues such as population trends, demand on urban services, levels of service
available, development right demand, infill potential, environmental and agricultural
resources, and above all concurrency, which demands that local government phase
development so it occurs only after urban facilities or infrastructure have been provided.
In December of 1996, the Miami-Dade County Board of County Commissioners
passed Resolution No. 1477-96 establishing an Infill Strategy Task Force to study
opportunities and strategies to promote infill within the UDB. The Task Force’s 1997
final report recommended, among other things, that the UDB not be expanded for at least
ten years and that the policy of discouraging infrastructure investment outside the UDB
be continued.
12Comprehensive Development Master Plan policies reflect the need to discourage
sprawl development outside the UDB in order to preserve agriculture. Policy 8G states
that the UDB should contain developable land having capacity to sustain projected
countywide residential demand for a total period of 15 years after adoption of the most
recent Evaluation and Appraisal Report.
13 Policy 8H further indicates that whenconsidering land areas to be added to the UDB, the Redland area (a prime agricultural
location) shall not be cons idered, and land designated for agricultural land uses on the
LUP shall be avoided.
14 The Comprehensive Development Master Plan also indicatesthat the principal uses in the “Agriculture” district should be agriculture and uses
ancillary to and directly supportive of agricultural. While uses ancillary and necessary to
agriculture may be permitted, the County should consider whether future schools should
8
MIAMI-DADE COUNTY, COMPREHENSIVE DEVELOPMENT MASTER PLAN at I-45 (2001).9
Id.10
Id. at I-46.11
MIAMI-DADE COUNTY ZONING CODE, Sec. 2-116.1. (2002).12
MIAMI-DADE COUNTY, supra note 8, at I-45.13
Id. at I-16.14
Id at I-17.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
6
be located outside the agricultural area within the urban development areas of the
County.
15Though some agriculturally zoned land exists within the UDB, no new
commercial agricultural use of property may be established within the boundary (though
limited exceptions exist).
16 This is consistent with a countywide strategy to maximizedensities and urban uses within the UDB and to maximize preservation of land values
within the community. Conversely, there are lands that are zoned agricultural within the
UDB but are re-designated for urban development pursuant to amendments to the
Comprehensive Development Master Plan in 1995. These lands shall be converted only
pursuant to policies within the Comprehensive Development Master Plan and contingent
on a Farmland Conservation Study.
17Residential development is only permitted at a density of one unit per five acres
(1:5). Smaller residential parcels may be created only if the immediate area surrounding
the subject parcel on three sides is predominately parceled in a similar manner and if
division of the subject parcel would not encourage further land division in the area.
18 Nobusiness or industry (with the exception of packing houses) is allowed in the Agriculture
district unless it is directly related to agricultural uses, is located on an existing arterial
roadway, and a adequate water supply and sewage disposal exists in accordance with
County law. Other uses compatible with agriculture and rural residential character may
be approved based on a determination of public necessity or public interest; or if the
applicant can prove no other suitable site exists outside the Agriculture district.
19B. Agricultural Land
There are approximately 1.55 million acres in Miami-Dade County, ¾ of which
are under water, in water conservation areas or considered submarginal for urban or
agricultural uses.
20 Agricultural uses in Miami-Dade County are located in the southcentral portion of the County, also known as the Redland. There are considerable urban
land uses scattered throughout this agricultural area.
According to the Census of Agriculture, land devoted to agriculture has remained
fairly stable since the 1980s, ranging from 83 to 87 thousand acres, or approximately 7
percent of total county acreage.
21 While the number of farms declined by 17 percent to1,576 since 1992, the acreage of land devoted to agriculture actually increased 1.7
15
Id. at I-47.16
Id at I-45.17
Id at I-46.18
Id.19
Id.20
ROBERT DEGNER, TOM STEVENS, DAVID MULKEY, & ALAN HODGES, FLORIDA AGRICULTURALM
ARKETING RESEARCH CENTER, ECONOMIC IMPACT OF AGRICULTURE AND AGRIBUSINESS IN MIAMI-DADEC
OUNTY, FLORIDA p. x (2000).21
Id.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
7
percent in the same period to 85,093 acres.
22 Agricultural land in Miami-Dade County isconsidered to be among the most threatened in the nation.
23Government agencies have played a significant role in the purchase of agricultural
land for conservation purposes. Between 1975 and 1998 over 10,300 acres of farmland
were purchased by governmental agencies, in particular by the South Florida Water
Management District (SFWMD). In 2000 it is estimated that the SFWMD leased
approximately 5,000 acres to private individuals.
24C. Economic Impact of Agricultural Land
Florida ranks in the top 10 states in total market agricultural value and its market
value per acre of farmland is also among one of the top ten producing states.
25 The totaleconomic impact from all agricultural sales originating in Miami-Dade County exceeded
$1.07 billion for the 1997-98 crop year. Fresh vegetable production was the largest
contributor to this total with nearly $491 million, or 45.6 percent of the total. The
greenhouse/nursery industry was responsible for nearly 41 percent or $439.8 million of
the total economic impact. Although sales revenues generated by nurseries and
greenhouses exceeded revenues for vegetables by over $7 million during this period, a
greater proportion of vegetables are shipped outside the County, thereby generating more
"new" dollars and a greater economic impact. Sales of tropical fruits produced in the
County created an economic impact of $137 million, representing about 12.7 percent of
agriculture’s value. Miscellaneous livestock sales, including aquaculture, generated an
economic impact of about $8.2 million, representing less than one percent (1%) of
agriculture's total economic impact.
Agriculture created an estimated 14,795 jobs in Miami-Dade County for 1997/98.
Agriculture's impact on earnings in Miami-Dade County totaled over $362 million for
1997-98. Approximately 46.5 percent, or $168 million, of this earnings impact was
generated by the vegetable industry. More than 42 percent, or approximately $153
million, was contributed by the greenhouse and nursery subsector. The tropical fruit
subsector generated nearly $41 million (11.2 percent) and miscellaneous livestock was
responsible for $450 thousand (0.12 percent) of agricultural earnings impact for Miami-
Dade County in 1997.
26D. Growth Management Challenges
Miami- Dade County must establish alternative development patterns to encourage
managed growth and preserve values of agricultural land. Growth management
techniques must preserve the value of agricultural land, the environment, and
development rights while protecting urban viability and stability.
22
Id.23
American Farmland Trust, Farming on the Edge (1997) available athttp://www.farmlandinfo.org/cae/foe2/
(July 31, 2002).24
DEGNER, supra note 20, at x.25
American Farmland Trust, supra note 23.26
DEGNER, supra note 20, at x-xi.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
8
Implementation of a program must be legally defensible. Statutorily, local
government is required to protect and preserve land and to mitigate impacts on
environmental lands.
27 However, in fulfillment of state mandate, private property rightsadvocates may view any scheme that reduces land values as a taking under the Fifth
Amendment of the U.S. Constitution, the Florida Constitution, or the Bert J. Harris Act.
28Governments must balance the need to protect health, welfare and safety with the
guarantee for compensation for land that is taken for public purposes. The land use
program for Miami-Dade County must strive to strike equilibrium between these
competing interests.
Agricultural preservation must be part of a wider comprehensive planning
program. Community input is vital to enhance the quality of planning. Agricultural
landowners bring specific information about their needs to the table. In the long run, a
plan that combines planning and agricultural knowledge will enhance the quality of the
plan. An extensive public input process will also help to avoid unnecessary contention
between self-interested parties, including urban and agricultural dwellers and the
government. An effective public input process allows interests to resolve their
differences prior to adoption of any plan, and to ensure that the plan addresses the needs
of different groups.
III. A
GRICULTURAL AND RURAL LAND POLICIES AND IMPLEMENTATION TECHNIQUESThis section focuses on techniques for agriculture and rural land retention. The
underlying goal is to: (1) achieve preservation of the lands most suitable for future
agricultural use; (2) achieve preservation of agricultural land values; and (3) preserve the
rural character of the area.
A. Agricultural Zoning
Zoning is the most utilized technique for preserving agriculture and rural lands.
Zoning land exclusively for agricultural uses prevents residential subdivisions while
simultaneously creating a holding zone to restrict urban expansion.
29Miami- Dade County has a specific zone, an AU zone, that allows agricultural and
related uses including packing facilities, outdoor storage of farming equipment, farming,
cattle grazing, hog and dairy farms (but only after approval at a public hearing),
nurseries, greenhouses, groves, truck gardens, single-family homes, schools, day cares,
and group homes. Minimum lot size for a residential lot is five acres.
27
Julian Conrad Juergensmeyer, James C. Nichols, & Brian D. Leebrick, Transferable Development Rightsand Alternatives After Suitum
, 30 URB. LAW. 441, 443 (1998).28
Id.29
ROBERT H. FREILICH, FROM SPRAWL TO SMART GROWTH: SUCCESSFUL LEGAL, PLANNING, ANDE
NVIRONMENTAL SYSTEMS 284 (American Bar Association 1999).Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
9
1. Area Based Zoning
Fixed area based zoning allows for one dwelling unit for a specified number of
acres. For example, the zoning ordinance in Lancaster County, Pennsylvania (See Task
2(c) Report) allows for one non-farm lot for every 50 acres. A non- farm lot subdivided
from its parent tract must be at least one acre, but not more than two.
30 Similarly, thequarter-quarter approach operates by splitting off land from the parent parcel, and
establishing a maximum or minimum parcel size for building lots.
31Sliding scale zoning is another agricultural protection technique in which the
number of dwelling units permitted varies with the size of the tract. Owners of smaller
parcels may divide their land into more lots on a per-acre basis than owners of larger
parcels.
32 Sliding scale zoning may also be used by qualitatively assessing land. Forexample, Clinton County, Indiana allows denser development on lands with poor soil
quality and prohibits development on lands with high soil quality.
33The rationale behind sliding scale zoning is to promote development on smaller
tracts that are on less valuable soil while prohibiting development on fertile, soil rich
lands.
34 High-density development also satisfies the legal requirement that municipalitiespermit some economically viable use of land when farming is not profitable.
35Critics of area based zoning suggest that a successful program must require that
properties be restricted with conservation easements to prevent further development after
the maximum density is reached.
36 Communities that do not require conservationeasements or some other type of deed restriction will be in danger of losing the land to
non-agricultural uses in the future. The other potential problem with area based zoning is
that, like any zoning ordinance, it only exists as long as the political will to maintain and
enforce it exists. Communities must be willing to commit to this type of zoning over an
extended period of time for it to be successful.
On the other hand, this type of zoning is a very inexpensive way to protect land
because little public expenditure is necessary. Compared to other programs such as
TDRs or PDRs (discussed below), zoning can be implemented very quickly, and,
furthermore, the public is accustomed to these traditional zoning techniques.
2. Large Lot Zoning
Some communities have tried to slow rapid growth patterns by requiring rural
land to be subdivided into lots no smaller than five or more acres, with the intention that
30
AMERICAN FARMLAND TRUST , SAVING AMERICAN FARMLAND: WHAT WORKS 59 (1997).31
METROPOLITAN MIAMI-DADE COUNTY PLANNING DEPARTMENT & METROPOLITAN MIAMI-DADEC
OUNTY COOPERATIVE EXTENSION DEPARTMENT, MANAGEMENT OPTIONS EVALUATED FOR THER
ETENTION OF LAND FOR AGRICULTURE IN DADE COUNTY, FLORIDA 76 (1981).32
AMERICAN FARMLAND TRUST , supra note 30, at 31733
Id.34
Id. at 60.35
Id. at 60.36
Id. at 59.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
10
larger parcels will maintain lower density and rural character. The intent also is to
protect water quality and environmental resources. As a rule of thumb, the minimum lot
size created is the amount of land necessary to carry on a successful farming operation,
thus, lot sizes reflect the economic reality of agriculture.
37Though large lot zoning was a traditional strategy to protect farmland in the 1970s
and 80s, the resulting development of subdivisions has suggested that it may not be the
most effective strategy. The main problem is that the lot size is not large enough to
discourage development, yet is too small for effective agriculture.
38Large lot zoning, therefore, is widely criticized for promoting sprawl and the
degradation of farmland. Large-lot zoning essentially converts farms and valued open
space into private property and large lawns, where little community open space is
preserved, and neighbors are isolated from each other by their islands of unproductive
private land. The resulting pattern becomes "wall- to-wall" subdivision, where every
portion of each parcel is developed into yards, roads, and driveways.
39 Many propertyowners object to large lot zoning because, they allege, “low- and moderate-income
homebuyers are excluded from this sector of the housing market”.
40 Some critics havedubbed large lot zoning “snob zoning”.
413. Cluster Zoning
Cluster zoning utilizes development on part of a property while preserving the
remainder for open space and/or agricultural uses. Cluster zoning requires more
creativity in urban site design and protects on-site amenities or environmentally sensitive
areas.
42 Cluster zoning is also known as “open space zoning” or “density zoning,” andcluster subdivisions are sometimes known as “cluster developments”, “open space” or
“open land subdivisions”.
43 Cluster zoning may allow variable lot sizes, setbacks,landscaping, densities, and design standards.
Clustering may be accomplished by the use of a particular zoning district that
establishes a fixed or sliding scale area-based dwelling unit allocation and requires
clustering on a portion of the site. Clustering can be used in conjunction with existing
zoning and allowed as an optional or density bonus.
44 For example, in the Hammocks, aclustered residential development in Florida, single-family housing was built by creating
green spaces within neighborhoods and a greenway system between the neighborhoods
37
METROPOLITAN MIAMI-DADE COUNTY PLANNING DEPARTMENT , supra note 31, at 73.38
TOM DANIELS, WHEN CITY AND COUNTY COLLIDE: MANAGING GROWTH IN THE METROPOLITAN FRINGE217 (Island Press 1999).
39
Jackson Meadow, Ecology of the Cluster Model, available athttp://www.jacksonmeadow.com/brochure/brochure/brochure_3.htm
(August 1, 2002).40
The Greenbelt Education Project, How to Keep the Country in the Lowcountry, available athttp://www.charleston.net/org/greenbelt/tools.html
(August 1, 2002).41
Executive Order 418 Housing Certification Commonwealth Of Massachusetts Fy2002, available athttp://www2.massdhcd.com/e418portal/ CommReport02.asp?MNO=317&FY=2002 (August 2, 2002).
42
METROPOLITAN MIAMI-DADE COUNTY PLANNING DEPARTMENT , supra note 31, at 77.43
AMERICAN FARMLAND TRUST , supra note 30, at 33.44
METROPOLITAN MIAMI-DADE COUNTY PLANNING DEPARTMENT supra note 31, at 77.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
11
and lakes. The Hammocks was also able to double their gross density to an average net
density of 11.5 units per acre.
45Cluster zoning may require the landowner of a tract of land to identify the
building lots and the open space to be preserved, or it may simply require that a certain
percentage of land remain as open space dedicated to agricultural uses. The protected
land is usually owned and maintained by a homeowners association. Permitted land uses
are either identified in the existing zoning or limited by cluster development regulations.
For example, one model ordinance permits residential uses such as clustered single
family houses, single family farmstead dwellings, and community living arrangements
and agricultural/open space uses such as farming (i.e. crops, farming, and livestock),
Christmas tree farming and sales, and passive recreational spaces (i.e. wildlife sanctuaries
and nature preserves).
46 Other communities, like Larimer County, Colorado, offer asystem of incentives and benefits that gives local administrators and land owners
flexibility to tailor land use requirements to the particularities of individual parcels of
property.
47However, the most effective clustering ordinances are those that are mandatory.
48When clustering and open space preservation are left optional, few developers take
advantage of the approach. Most continue as they have always done: creating
checkerboards of house lots and streets. This means that even though the clustering
option is in the zoning ordinance, it remains essentially unused. The community is still
left with conventional development patterns which destroy agricultural areas.
49Though cluster zoning can keep land available for agriculture or open space, it is
generally not a viable technique for commercial agriculture.
50 The protected land isgenerally owned by a homeowners association, and while homeowners may lease it back
to local farmers, some residents may object to allowing agricultural production because
of noise, dust, and odors related to commercial farming.
51 Utilization of right-to-farmlaws (discussed below) will help. One solution creates an ordinance that requires
homeowners to lease the land back to local farmers, while limiting the type and scale of
agriculture on the property, or ensuring that farmers who sell development rights to
homeowners retain title to continue farming.
52 In general, cluster zoning has been usedmost successfully to preserve open space or to create transitional areas between farms
and residential areas.
5345
Sprawlwatch, Land Use Planning and Zoning, available athttp://www.sprawlwatch.org/landuseandplanning.html
(August 1, 2002).46
Southeastern Wisconsin Regional Planning Commission, Model Zoning Ordinance for Rural ClusterDevelopment
, available at http://www.sewrpc.org/modelordinances/cluster_ordinance.pdf (August 1,2002).
47
E. Tyson Smith & Philip Moffat, An Analysis of the Development and Planning Alternatives to Protectthe Character of Eastern Sarasota County while Minimizing Adverse Impacts on Taxpayers
32 (January2000) (unpublished manuscript, on file with the University of Florida Conservation Clinic).
48
Id. at 32 (referencing SAMUEL N. STOKES, ET AL., SAVING AMERICA’S COUNTRYSIDE 182 (2nd Ed. 1997)).49
Randall Arendt, “Open Space” Zoning: What it is and Why it Works, 5 PLAN. COMMISSION J. 4 (1992),available at
(http://www.plannersweb.com/articles/are015.html#mandatory) (August 2, 2002).50
AMERICAN FARMLAND TRUST , supra note 30 at 33.51
Id.52
Smith, supra note 47, at 31.53
AMERICAN FARMLAND TRUST , supra note 30 at 33.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
12
Critics of cluster zoning argue that it actually results in “clustered sprawl”.
54Critics also argue that cluster zoning is environmentally unsound because cluster
development works best with urban infrastructure, but the remote location requires onsite
septic tanks. Failing septic systems require the extension of water and sewer lines,
which opens farmland up to more development.
55 Finally, cluster development sometimesis criticized based on the simple presumption that residential and agricultural uses cannot
exist in close proximity without unacceptable conflict.
56 Clearly, as mentioned above,certain conflicts must be addressed. Crop dusting and spraying, for example, require that
significant buffers between crops and clustered homes be maintained.
Critics of clustering worry that this technique will cause loss of rural character.
However, subdivisions designed with this concern in mind can mitigate, if not eliminate,
this concern. For example, instead of having separate driveways onto the arterial roads,
creating a more urban feel, a subdivision could be designed so the entire tract is set back
from the main road, and only one access point exists to the road, with houses accessing a
loop or networks of small streets. Those streets should be gravel and narrower than
traditional urban subdivisions to create a rural neighborhood feel.
Subdivisions also should be buffered from the street with extensive landscape
material; perhaps so well-buffered that passing motorists are not aware that the houses
exist. If there are wooded or heavily landscaped areas, the cluster should locate within
the wooded areas
The design of the building within the community can also reduce any concerns.
Houses can be designed to connote a small town feeling instead of the spreading suburbs.
Architects may design homes with human proportions, local architectural styles, local
materials, and other techniques to connect the house to the particular community.
57Clustered developments are allowed in Miami-Dade County under its Zoning
Code.
58 Cluster developments must be single-family dwelling units and common areasare allowed within the zone, including any associated structures.
4. Buffering
Buffering is the physical separation of farms from incompatible uses, usually by
landscape, open space, or other barriers. Buffers are narrow bands of land planted with
permanent vegetation that are located around and in areas of intensive agricultural
production.
59 Buffers help safeguard farms from trespassers and protect adjacent54
DANIELS, supra note 38, at 219.55
Id.56
Id. at 219.57
RANDALL ARENDT ET AL., RURAL BY DESIGN: MAINTAINING SMALL TOWN CHARACTER 62 (PlannersPress 1994).
58
MIAMI-DADE COUNTY ORDINANCES 33-284.6-.9.59
National Conservation Buffer Council, Conservation Buffers: Showing Stewardship, ProtectingProductivity
, available at http://www.buffercouncil.org/ (August 1, 2002).Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
13
homeowners from the externalities of commercial farming.
60 Field borders, grass buffers,contour grass strips, grassed waterways, and vegetative borders, are several types of
buffers which serve to minimize conflicts between residential and agricultural users.
61Buffers are advantageous for many other reasons. Buffers create havens for
wildlife. Buffers are visible, tangible examples of land stewardship.
62 Buffers enhancequality of life by providing open space in a community and enhancing the value of land
conservation. Environmentally, buffers slow down water runoff from fields and block
suspended chemicals, pathogens, and sediment from reaching water bodies.
63Buffering places the responsibility for construction and maintenance upon the
farm owner, the adjacent homeowners or a third party. The Georgia Model Code, for
example, requires any non-agricultural use locating next to an agricultural use to provide
a 150 foot agricultural buffer.
64 The buffer must consist of trees, hedges, landscaping,and naturally occurring elements as long as there is a semi-opaque screen between the
agricultural and non-agricultural uses.
65 Many California localities similarly requireagricultural setbacks. In San Luis Obispo County the buffer is mandatory and ranges
from 100 to 800 feet depending on the type of agricultural use to be protected. In
Sacramento County the buffer is mandatory and generally requires a physical separation
of 300 to 500 feet. In Stanislaus County the buffer is mandatory and can be
topographical, vegetative or other and is determined on a site-by-site basis.
66Some buffers are not mandatory but are farmer initiated. In Suffield, Connecticut
an individual farmer may request a buffer with a width of 30 to 100 feet. The buffer is
located on the parcel to be developed and maintained by the developer. The law also
requires that lot owners be notified that they are responsible for buffer maintenance and
that subdivision plans include a provision for active agriculture and recognize agricultural
practices that may annoy or irritate residents.
67The Natural Resources Conservation Service (NRCS), of the United State
Department of Agriculture (USDA), promotes the development of buffers by farmers
themselves. The NRCS leads the National Conservation Buffer Initiative, a multiyear
effort undertaken by the USDA. The goal of the initiative is to encourage the use of
conservation buffers by farmers, ranchers, and other landowners as a means of improving
soil, water, and air quality while enhancing fish and wildlife habitat, and adding to the
60
AMERICAN FARMLAND TRUST , supra note 30, at 318.61
National Conservation Buffer Council, Conservation Buffers: Showing Stewardship, ProtectingProductivity, available at
http://www.buffercouncil.org/ (August 1, 2002).62
Id.63
Id.64
Georgia Department of Community Affairs, Model Code: Alternatives to Conventional Zoning:Agricultural and Buffer Requirements §4-3 (April 2002),
available athttp://www.dca.state.ga.us/planning/ModelCode/4-3AgriculturalBuffer.pdf
(August 1, 2002).65
Id.66
Farmland Preservation Report, Farmland Programs Neglect Buffer Protections, Volume12, Number 4,(February 2002).
67
Id.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
14
beauty and diversity of farms and ranches across the country.
68 Farmers can receiveassistance through the Conservation Reserve Program and other federal, state, and local
government programs to help with the cost of implementing buffer practices. These other
programs include the Environmental Quality Incentives Program, Wildlife Habitat
Incentives Program, Wetlands Reserve Program, and Stewardship Incentive Program.
69A significant challenge with buffers is enforcement. Though ordinances may
require buffers, they are not always enforced. Buffering ordinances can be effective as
long as local government has subdivision review authority to impose the buffer
requirement and that they are enforced once in place. Placing the buffer restriction in the
landowner’s title will assure adequate legal notice to the individual land owner
responsible.
70Successful buffer ordinances cannot be standard; each buffer must be site based
and locally determined. A draft report from a California research group indicates that in
some cases structural barriers are actually more effective than swathes of open space.
Under this scenario, an ordinance must determine the structural barrier and establish a
source of payment for repairs and maintenance
715. Overall Benefits and Drawbacks of Agricultural Zoning
Overall, the aforementioned zoning techniques are an inexpensive way to protect
large areas of agricultural land because little public expenditure is necessary to
implement zoning ordinances. Communities also favor agricultural zoning ordinances
because they are easy and quick to implement as compared to TDR or PDR programs
(discussed below) and easy to explain to the public who are accustomed to zoning
ordinances. They also separate farms from non-agricultural land uses, and reduce the
likelihood of conflicts between farmers and non- farming neighbors. Finally, agricultural
zoning is flexible in that it can change wit h the economic or political climate.
72Critics of agricultural zoning suggest that such programs are not permanent.
While flexibility may be a benefit it is also a drawback because large agricultural parcels
may quickly be converted to developable parcels. Similarly, agricultural preservation
ordinances do not prevent annexation by municipalities (unless annexation is forbidden
on agricultural lands). Many successful agricultural zoning programs have a mandatory
deed restriction or easement requirement to prevent conversion when annexation occurs.
These ordinances also generally decrease land values, which decreases a farmer’s equity
in land. For this reason, many farmers oppose these programs. Finally, such programs
may be difficult to monitor and enforce on a day-to-day basis.
7368
United State Department of Agriculture, Farm Preservation Report: Buffers, Common-SenseConservation, available at
http://www.nrcs.usda.gov/feature/buffers/BufrsPub.html#InitiativeBuff_7Anchor
(August 1, 2002).69
Id.70
Farmland Preservation Report, supra note 66, at 2.71
Id. at 3.72
AMERICAN FARMLAND TRUST , supra note 30, at 50.73
Id.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
15
B. Non-Zoning Techniques
1. Right-to-farm Laws
Since 1963, every state in the nation has enacted a right-to-farm law.
74 Right-tofarmlaws are state laws or local ordinances that protect farmers and farm operations from
public and private nuisance law suits.
75 The right-to-farm laws strengthen the legalposition of farmers against nuisance suits by their neighbors, and protect farmers from
anti-nuisance ordinances and unreasonable agricultural regulations.
76 Right-to- farm lawsdo not protect farmers from state and federal pollution and safety laws, but do underscore
the legitimacy of farm uses.
77State right-to- farm statutes can be broken into three groups. First,
general rightto-farm statutes provide that a farming operation cannot be declared a nuisance if it was
not a nuisance at the time the operation began.
78 This type of statute is also termed a“coming to the nuisance” statute. It gives farmers a legal defense from residents moving
to the area who claim to be harmed by the off-site impacts of agriculture.
79 The secondtype of statute protects specific types of agriculture such as the cultivation of land,
production of crops, and raising of poultry.
80 These types of statutes protect farmers fromunreasonable local regulations. The third type of statute protects farmers and food
companies from suits over food safety.
81 Florida’s Right-to-Farm Act, which applies inMiami- Dade County, is a general right-to- farm law.
Right-to-farm laws have not been extensively litigated, but this is likely to change
as the urban fringe creeps nearer to farmland and new residents file suits based on
trespass rather than based on nuisance.
82 Plaintiffs may still file a nuisance suit against afarmer regardless of the existence of right-to-farm laws. Though the plaintiff has a slim
chance of winning, the cost and aggravation of the suit may be detrimental to the farm.
83Thus, some statutes, for example Michigan, require plaintiffs to pay farmer’s costs in an
unsuccessful nuisance suit,
84 while states such as Delaware, Iowa, Kentucky, Missouri,New Mexico, South Dakota, and Wisconsin allow farmers to recover only for frivolous
suits.
8574
Id. at 169.75
A public nuisance involves actions that injure the public at large, while private nuisances interfere withan individual’s use of their property.
76
AMERICAN FARMLAND TRUST , supra note 30, at 169.77
DANIELS, supra note 38, at 220.78
DAVID L. CALLIES, ROBERT H. FREILICH, & THOMAS E. ROBERTS, CASES AND MATERIALS ON LAND USE662 (3
rd ed. 1999).79
DANIELS, supra note 38, at 175 (citing NEIL HAMILTON, A LIVESTOCK PRODUCER’S LEGAL GUIDE TON
UISANCE, LAND USE CONTROL AND ENVIRONMENTAL LAW (Drake University Agricultural Law Center1992)).
80
FREILICH, supra note 29, at 287.81
Id.; Melody Petersen, Farmers’ Right to Sue Grows, Raising Debate on Food Safety, N.Y. Times, June 1,1999 at A-1, col. 1.
82
DANIELS, supra note 38, at 150.83
Id. at 151.84
Id.85
Id. at 176-79.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
16
Right-to-farm laws are effective when metropolitan areas begin to encroach on
outlying farm communities.
86 They make urban dwellers that want a rural lifestylerethink their decision when animal waste, airborne pollution, odors, slow-moving farm
machines on roads, and roosters crowing at the crack of dawn disturb their “rural
tranquility”.
87 Without such laws, public law nuisance suits may succeed. As a politicalmatter these ordinances also encourage elected officials to minimize ordinances that are
intrusive on farming. Nonetheless, these laws do not prevent the ultimate problem of
incompatibility of uses, which must be addressed through strict environmental
enforcement and well-designed agricultural districts. Another resolution is to allow for
payment of damages instead of cessation of activities.
88One County Commissioner in Larimer County, Colorado suggested a creative
“right-to- farm” provision. He drafted the
Code of the West, which provides advice forpeople thinking of buying land in the rural part of Larimer County’s metropolitan region.
The introduction says:
It is important for you to know that life in the country is different from life in the
city. County governments are not able to provide the same level of service that
city governments provide. To that end, we are providing you with the following
information to help you make an educated and informed decision about whether
to purchase rural land.
89The
Code of the West then goes on to describe the realities of country life,including slow tractors, that some lots are not buildable, that farmers work around the
clock and that animals and manure can cause objectionable odors.
90Right-to-farm laws strengthen growth management techniques such as clustering.
In a recent case,
Whitted v. Canyon County Board of Commissioners,91 the Iowa SupremeCourt concluded that right-to-farm laws encourage full and complete use of agricultural
land, yet are still compatible with growth management techniques. A farmer proposed a
small subdivision on a portion of his farm with rocky, poor farmland. He intended to
continue farming the rest of the land. Neighbors appealed the approval of the subdivision
claiming it would deprive them of full use of their agricultural land. The court disagreed
and concurred with the county’s land use board, stating “[by] allowing development…the
development pressure on land more conducive to agriculture would be lessened.
Further…requiring deed restrictions and marketing disclosures would aid in preserving
the agricultural nature of the surrounding area.”
92Section 33-28.1 of the Miami-Dade County Zoning Code requires agricultural
disclosures for any land that is either designated Agriculture (AU), or zoned Interim (GU)
(outside UDB only) and determined to be subject to AU trends of development or located
within the UDB and abuts any AU zoned parcel. The seller of such property must inform
86
FREILICH, supra note 29, at 287.87
Id.88
See e.g. Boomer v. Atlantic Cement Co., Inc., 40 N.Y.S.2d 97 (N.Y.Sup. 1972).89
DANIELS, supra note 38, at 275.90
Id. at 275-78.91
44 P.3d 1173 (Idaho 2002).92
Id. at 1178.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
17
the buyer that the land or adjacent land is zoned agricultural and that there are associated
noises, pollutants, and activities that might be offensive to the buyer.
The Florida Right-to-Farm-Act prohibits farms in operation for a year or more
from being declared either a public or private nuisance, except under very limited
circumstances. In order to enjoy protection under the Act, however, the farm must
continue to comply with “generally accepted agricultural and management practices”.
93The Second District Court of Appeals for the State of Florida found that the right-to-farm
law was “intended to preserve productive land for agricultural purposes and to protect the
established farmer from demands of sprawling urban development.”
94 However, verylittle litigation has occurred pursuant to this law since its original adoption in 1979.
2. Agricultural Districting
Agricultural districting is different than agricultural zoning. Zoning only
addresses particular land uses and is one tool that can be used in an agricultural district.
Agricultural districting, on the other hand, allows farmers to form special areas
where commercial agriculture is encouraged and protected, establishing a broad array of
measures to encourage and protect agricultural activity in the district.
95 Protectivemeasures may include bans on local government laws that restrict farming, enhanced
protection from private nuisance lawsuits, eligibility for differential tax assessment,
limiting non-farm development around active agricultural areas and conservation
easement programs.
96 Pennsylvania created one of the most effective agriculturaldistricting programs in the country. The Pennsylvania law identifies five purposes for
agricultural districting: “(1) Encourage landowners to make a lo ng term commitment to
agriculture by offering them financial incentives and security of land use; (2) Protect
farms from incompatible uses; (3) Assure permanent conservation of agricultural land to
protect the agricultural economy; (4) Provide compensation to landowners for
development rights; and (5) Leverage state funds for the purchase of agricultural
conservation easements and protects [sic] the public investment in easements.”
97Agricultural districting programs are generally state-level programs. To date,
sixteen states have enacted agricultural district laws.
98 Generally, state statutes establish aprocess for identifying agricultural districts and designate geographical areas for long
term agriculture. State statutes also include a combination of measures and management
tools, as described above, to protect farmland. The requirements and provisions of the
programs differ greatly, but general conclusions can be drawn. The programs are flexible
and local in nature, stabilize the land base at a low public cost, provide multiple benefits
93
Fla. Stat. 823.14.94
Pasco County v. Tampa Farm Service, Inc., 573 So. 2d 909 (2nd DCA 1990).95
AMERICAN FARMLAND TRUST, supra note 30, at 197; METROPOLITAN MIAMI-DADE COUNTY PLANNINGD
EPARTMENT , supra note 31, at 94.96
Id.97
AMERICAN FARMLAND TRUST , supra note 30, at 201.98
Id. at 197.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
18
to farmers, help protect large blocks of land, and enrollment is voluntary.
99 In contrast,drawbacks associated with agricultural districting include the fact that sanctions for
withdrawing land are minimal and do not deter conversion; the limits on non-farm
development may not prohibit the development of urban infrastructure in agricultural
areas; in some states, the benefits are not a strong enough incentive for farmers to enroll;
and, in others, the procedure for creating the districts is long and cumbersome.
100 Floridadoes not have a similar state law, but that does not preclude Miami-Dade County from
implementing some agricultural districting measures typical in state- level programs.
New York has one of the most successful agricultural districting programs in the
nation, in part because it is aimed at preserving farmland through maintaining and
fostering farming itself. By granting a series of benefits that provide more favorable
social and economic conditions, the program encourages an environment that is more
beneficial for agriculture. Support from elected officials also has helped to create an
agriculture- friendly atmosphere. For example, the legislature passed an act that declares
agricultural land to be an “environmental resource of major importance”.
101In addition to creating an agricultural districting program, the New York program
also includes provisions that prohibit local nuisance ordinances from interfering with
normal farm operations; requires agency review of development which induces
infrastructure expansion; requires alternative consideration for public development
proposals that bring agricultural lands into the hands of the municipality through eminent
domain; allows for tax incentive programs; and directs all state agencies to maintain
viable agricultural districts.
1023. Land Evaluation Systems
The land evaluation and site assessment system (LESA) was launched in 1981 by
the U.S. Soil Conservation Service to make objective ratings of the agricultural suitability
of lands against demands for other uses.
103 LESA effectively rates a tract’s potential foragriculture, as well as other social and economic factors.
104 Though the federalgovernment developed LESA, state and local governments have adopted it to meet their
specific needs, and it has become part of many governments’ land use planning tools.
105LESA enables the planning of water, sewer, and transportation projects or the creation of
agricultural districts, and the assessment and review of environmental impacts.
10699
Shirley Sternamen & Elizabeth Mumby, New York State: Protecting Farming with Agricultural Districts77, 80,
in PLOWING THE URBAN FRINGE: AN ASSESSMENT OF ALTERNATIVE APPROACHES TO FARMLANDP
RESERVATION (Hal Hiemstra & Nancy Bush wick, eds., 1989).100
Id.101
Id. at 86.102
Id. at 80; see also N.Y. AGRI. & MKTS. LAW § 300 et. Seq. (1988 Cum. Supp.).103
Frederick R. Steiner, Introduction, in A DECADE WITH LESA: THE EVOLUTION OF LAND EVALUATIONAND
SITE ASSESSMENT 13 (Frederick R. Steiner, James R. Pease & Robert E. Coughlin eds., 1994).104
Id.105
Id.106
Lloyd E. Wright, The Development and Status of LESA, in A DECADE WITH LESA: THE EVOLUTION OFL
AND EVALUATION AND SITE ASSESSMENT 36, supra note 103.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
19
LESA’s land evaluation and site assessment elements form a two-part system that
assists in the implementation of the Farmland Protection Policy Act (FPPA), selecting
appropriate lands to be included in the program, and establishing minimum parcel sizes
for farm subdivisions in agricultural districts.
107 The land evaluation part of LESA isusually designed by the federal Soil Conservation Service (SCS) and local Soil and Water
Conservation Districts (SWCD), and implemented by a local committee generally
comprised of a district conservationist, a cooperative extension representative, SWCD
directors, farmers, planners, local agricultural officials, and others who have knowledge
of the land resources of the area.
108Local officials or a locally appointed site assessment committee usually design
the site assessment component.
109 Site assessment factors include parcel size; on-farminvestment; and characteristics external to the parcel of land, such as nearby land uses,
zoning, and other farmland protection measures.
110 A local committee may include localplanners, members of the planning commission, SWCD directors, a cooperative
extension representative, building industry representatives, recreational representatives,
public interest groups, concerned citizens, and other government representatives
interested in agricultural preservation.
111LESA is a flexible system, designed to accommodate differences among states,
counties, or areas. Specific systems should be based on existing knowledge of the area,
local soil surveys, land use plans, policies, and programs. LESA may be applied
consistently to all lands or on a case-by-case basis.
112 LESA may be used to accomplishthe following objectives:
113i. Select lands to be part of a TDR or PDR program;
ii. Implement the federal Farmland Protection Policy Act;
iii. Choose farm units to be included in agricultural preservation programs;
iv. Determine appropriate lot size for subdivisions in agricultural districts;
v. Plan water, sewer, and transportation projects or the creation of
agricultural districts;
vi. Determine the need for an agricultural preservation program and the types
of programs to be used;
vii. Assess and review environmental impacts; and
viii. Develop guidelines under which agricultural land conversion to nonagricultural
uses should be permitted.
A 1990-91 study identified 212 local and state governments in 31 states as active
or former users of LESA.
114 Of these 212 jurisdictions, 138 local and state governmentswere still using the system in 1994. Those who abandoned the sys tem found it too
107
FREILICH, supra note 29, at 286.108
WRIGHT, supra note 106, at 35.109
Id.110
Id.111
Id. at 35-36.112
Id. at 36.113
Id.114
Id. at 58 referencing Steiner, F., J Pease, R. Coughlin, J. Leach, C. Shaw, A. Sussman, and J. Pressley.Agricultural Land Evaluation and Site Assessment: Status of State and Local Programs
(The HerbergerCenter 1991).
Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
20
complicated or time consuming; some noted a lack of interest or support by landowners
or planners.
115 The unreliability may be attributed to technical problems with a particularLESA system, staffing inadequacies, or local political factors.
116 Seventy- nine percent ofrespondents were satisfied with the LESA system.
Miami-Dade County does not have a LESA program, but other counties in Florida
– Highlands, Marion, and Pasco, for example – have utilized LESA. Although soil
quality, a major factor under LESA, is not as relevant in Miami-Dade County, other
LESA criteria will be useful should the County adopt prioritization criteria to implement
the preferred development scenario.
C. Land Acquisition Programs
1. Conservation Easements
A conservation easement (or conservation restriction) is a voluntary legal
agreement between a landowner and a land trust or government agency that permanently
limits uses of land in order to protect its conservation values. It allows a landowner to
continue to own and use their land and to sell it or pass it on to heirs.
117 Each easement istailored to meet the owner’s personal management objectives and goals for the property.
In essence the landowner sells his or her right to develop the land to a
conservation organization or governmental entity. Current uses, including residential and
recreational uses, agriculture, forestry, and ranching can continue, although the easement
might require the protection of some environmental and aesthetic qualities of the
property.
118Placing an easement may result in property tax savings and can be essential for
passing land on to the next generation. By removing the land's development potential,
the easement lowers its market value, which in turn lowers estate taxes. Whether the
easement is donated during life or by will, it can make a critical difference in the heirs'
ability to keep the land intact.
1192. Purchase of Development Rights
In a typical purchase of development rights (PDR) program, the government
purchases the owner’s right to develop specific parcels of land for managerial purposes,
leaving the owner all the rights of ownership.
120 One form of PDR commonly used foragricultural preservation is a purchase of conservation easements (PACE).
121 Landowners115
Id. at 59.116
Id.117
Land Trust Alliance, Conservation Options for Landowners: Conservation Easements, available athttp://www.lta.org/conserve/options.htm
(August 1, 2002).118
University of Florida, Conservation Easements, available athttp://www.sfrc.ufl.edu/Extension/ffws/ce.htm
(August 2, 2002).119
Id.120
See Thompson, Purchase of Development Rights: Ultimate Tool for Farmland Preservation?, 12Z
ONING & PLAN. L. REP. 153 (1989).121
The term PDR will encompass PACE for the remainder of this paper.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
21
sell conservation easements to governments or other private conservation agencies. The
price of the development right is generally equal to the diminution in the market value of
the land resulting from the removal of the development rights, and thus is the difference
between the value of the land for agricultural use or open space and the land’s
development value.
122 In return for the payment, the landowner agrees to use the land foropen space or agriculture in perpetuity, though some programs allow termination of the
condition under certain restrictions.
123PDRs are designed to be voluntary. Offering an incentive to land owners may
convince them to resist selling their land for a potentially high price to subdivision
developers. In short, purchasing development rights is cheaper than buying the land in
fee simple.
State and local governments may cooperate on PDR programs or work
independently. Some states have enacted PDR programs that are funded, implemented,
and administered by state agencies. Other states fund the purchase of land by either local
governments or non-profit organizations.
124 Cooperative programs are advantageousbecause they allow the state to set broad policies and implement regional planning
strategies. Local governments, with their specific knowledge of the area, then identify
land suitable for the PDR program and monitor the land once the easements are in
place.
125 Cooperative programs generally increase the level of funding available forPDRs.
According to the American Farmland Trust, PDR programs are very popular with
farmers, yet the supply of money has lagged behind the supply of easements offered by
farmers. PDR programs are popular with farmers because they offer enticing incentives.
PDR programs increase the availability of real capital to farmers without mortgaging
land; lower real property taxes due to the decrease in the value of the land once the
development rights have been sold; and there are potential estate or inheritance tax
benefits.
126 PDR programs offer a more permanent solution than zoning and avoid thetakings challenges that hamper zoning efforts.
127On the downside, some landowners reject PDR programs because they are
perceived as “tying the hands” of the landowners’ heirs, who may wish to sell the land
for development value.
128 In addition, although buying development rights is cheaperthan buying the property outright, a PDR program is still cash intensive and communities
may reject PDR programs if they require local monetary support in the form of
development fees or taxes. In communities where taxes and fees are already levied for
schools, public safety, parks, infrastructure, and community programs, agricultural
122
FRANK SCHNIDMAN, MICHAEL SMILEY & ERIC G. WOODBURY, RETENTION OF LAND FOR AGRICULTURE:P
OLICY PRACTICE AND POTENTIAL IN NEW ENGLAND 18 (Lincoln Institute for Land Policy 1990).123
See, e.g., MASS. ADMIN. CODE Tit. 330 Section 22.10 or RI Gen Laws Section 42-82-5e.124
See, e.g.,: Frank Schnidman, supra note 122, Rhode Island 204-5, Vermont 141-43, Connecticut 186,Maine, 306 and Massachusetts 88-91.
125
Id.126
PATRICIA E. SALKIN, ZONING AND LAND USE CONTROLS § 56.04[2] (2000).127
DANIELS, supra note 38, at 223.128
SALKIN, supra note 126, at § 56.04[2].Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
22
preservation may fall by the wayside unless there is heightened community awareness of
the necessity of preserving agricultural lands.
129Successful PDR programs must be carefully designed and include a set of criteria
to determine from which lands the development rights should be purchased. The criteria
must take into account the location and surrounding uses of the land. PDR programs
make sense if hundreds of acres can be preserved (either through contiguous smaller
parcels or a few large parcels) because it makes it more likely that commercial farms will
be successful.
130 If only smaller amounts of farmland can be preserved, the adjacent landmay be a magnet for housing developers who market “rural lifestyles” and the conflict
between farming and residential uses will be maximized.
131 Additionally, the costs ofland in PDR programs must be reasonable and should be balanced against the likelihood
that land will remain in viable agricultural production for a certain amount of time.
132 Ata high expense per acre, little farmland will be saved at enormous costs, and even then
the aforementioned issue arises of whether the farm will be big enough to sustain itself.
133Although Miami-Dade County has a viable “transferable development rights”
program (discussed below), known as “severable use rights” it does not have a PDR
program. The advantages of a PDR program are that the governing agency – or a
designated land trust – has greater control over which lands are identified for
preservation. The challenge, of course, is generating the funds to purchase development
rights. However, in communities that are experiencing a decrease in agricultural viability
and simultaneous increase in urban growth pressure, the ability to affirmatively secure
open space is critical to success. As is discussed in Task 2(c), this has proven to be the
case in many communities around the country that have successfully preserved
significant agriculture and open space lands. The Task 2(c) report explores five of these
communities and suggests ways that Miami-Dade County might successfully implement
similar regulatory approaches.
3. Land Banking
Land banking, also referred to as advance acquisition, is a technique where land is
purchased before it is ready to be developed.
134 This requires the establishment of landbanks for the purpose of acquiring lands in urban areas where expansion is expected to
ensure that it is developed at the most advantageous time for the community.
135 The landbanks are governmental units that could either purchase agricultural land in fee simple
and lease it back to farmers or only purchase the development rights.
136129
RICK PRUETZ, SAVED BY DEVELOPMENT: PRESERVING ENVIRONMENTAL AREAS, FARMLAND ANDH
ISTORIC LANDMARKS WITH TRANSFER OF DEVELOPMENT RIGHTS 69 (Arje Press 1997).130
DANIELS, supra note 38, at 224.131
Id.132
SALKIN, supra note 126, § 56.04[2].133
DANIELS, supra note 38, at 224; see also the discussion of Suffolk County in Task 2(c).134
DANIELS, supra note 38, at 171.135
FREILICH, supra note 29, at 290.136
FREILICH, supra note 5, at 42.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
23
Land banks are advantageous because they allow for better control over timing
and type of development, and discourage land speculation and leapfrog development.
137Also, by giving public officials a more personal interest in property and its regulation, it
helps promote sounder planning practices such as unrestricted, flexible comprehensive
plans. A land bank is flexible because it controls the land being sold and bought.
138A successful land bank must have the power to purchase property and condemn
land.
139 A land bank should be granted the power to hold land for an indefinite amount oftime so that the land bank can pace development appropriately. A land bank must also
have the power to borrow money, issue bonds, and obtain government aid.
140 The majordrawback to this technique is the expense.
The legality of land banking has been questioned, and the U. S. Supreme Court
has not established a bright line rule.
141 Both state and federal courts have declared that ifthe purpose of condemning the land has a reasonable relationship to the purpose of
protecting open space and environmental lands, then the taking is for a public use and
legitimate.
142 Land banking is more likely to be upheld by courts than other planningcontrols because it is a reasonable means of fulfilling a public purpose, particularly where
purchases are made consistent with the explicit policies of an adopted comprehensive
plan.
4. Transfer of Development Rights
Transfer of development rights (TDR) programs – called “Severable Use Rights”
in Miami-Dade – allow for planning on an area wide basis by allowing landowners in
restricted areas (“sending areas”) to transfer densities and other development rights to
landowners in areas appropriate for higher density development (“receiving areas”).
143Landowners in receiving zones are allowed to develop their land but only if they
purchase development rights from designated sending areas. Thus, development is
directed away from agricultural or environmentally sensitive lands to areas better
equipped to deal with heavy development.
144 TDR programs give governments analternative to purchasing land outright and ameliorate the harshness of restrictive
zoning.
145TDR programs are popular with citizens and governments because the goal is to
have an “everyone wins” outcome.
146 The sending site landowner is able to continuefarming without development pressures but with the benefits from the sale of the rights.
137
DANIELS, supra note 38 at 171.138
FREILICH, supra note 29, at 291.139
Id.140
Id.141
Id. at 292.142
Id.143
Id at 288.144
Andrew J. Miller, Transferable Development Rights in the Constitutional Landscape: Has Penn CentralFailed to Weather the Storm?
39 Nat. Resources J. 459, 467.145
FREILICH, supra note 29, at 288.146
PRUETZ, supra note 129, at 3.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
24
The receiving site landowner is able to build at a greater density, and realizes the market
value of their land. The community benefits by preserving farmland without incurring
significant expense.
147 Local governments particularly find these programs attractivebecause:
148·
They encourage increased densities in developed areas making full use of publicinfrastructure;
·
Increased density works together with the need to provide a fair share ofaffordable housing;
·
Often, private developers pay landowners, so no public monies are spent;·
Landowners receive compensation for the restrictions placed on their lands, thusdecreasing the likelihood of successful taking claims; and
·
Local government can preserve a significant amount of land while funnelinggrowth into desired areas.
TDR programs are a market-based tool, thus municipalities must be certain there is a
market for the development rights being bought and sold. A municipality must, through a
comprehensive planning process, determine how many development rights are to be
bought and sold and where. A TDR program must encourage sales that benefit the entire
community, not just a few select landowners.
149 The number of rights to be bought orsold should be based on ecological and populations concerns; the more sprawling the
community, the more rights are required.
150Successful TDR programs include the following:
·
Encouragement of sending area landowners to sell their development rightsthrough development restrictions, development constraints, and transfer ratios;
151·
Encouragement of receiving area landowners by allowing the highest densityappropriate, exemption from certain fees, and exemption from certain
development standards;
·
A clear separation between resource lands, existing development, and propertiesplanned for development;
152·
An active real estate market to ensure buying and selling of rights;153·
Fast, easy and certain TDR approvals, including certain costs, and a clear,discernible, and transparent process
154·
A TDR bank or revolving fund that can help set a floor price for TDRs155·
Provision of public staff for implementation;·
Monitoring of program performance; and·
A flexible program that can be refined as needed.TDR programs may be mandatory or voluntary. Mandatory programs are
designed to prevent fragmentation of farmland in a way that protects landowners’
147
Id.148
DANIELS, supra note 38, at 225.149
Id. at 51; FREILICH, supra note 29, at 289.150
FREILICH, supra note 29, at 289.151
PRUETZ, supra note 129, at 51.152
DANIELS, supra note 38, at 226.153
Id.154
PRUETZ, supra note 129, at 58.155
Id. at 61.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
25
equity.
156 Mandatory programs often feature dual zones with the down zoning of asending area and the designation of a receiving area. Landowners in the sending zones
are not required to sell their development rights, but may as a method of receiving
compensation for the down zoning. Similarly, receiving area landowners must buy
development rights to recognize the full economic potential of their land.
157 Mandatorydevelopment restrictions may include virtual prohibition of non-farm development in
agricultural areas through zoning, large minimum lot size, or restrictive requirements for
infrastruc ture.
158 Local governments implementing mandatory programs must ensure thatadequate public facilities will be available in the receiving areas.
159Voluntary TDR programs allow landowners in sending areas to sell their
development rights to a party in a receiving area in lieu of development in the sending
area. There is no reduction in density in the sending area.
160 Landowners in sendingareas may choose to develop parts of their property and sell off development rights on
another part, but this may lead to a large number of rural residences amid farmlands.
161Voluntary programs may be more attractive to local governments because they are less
politically controversial.
Successful TDR programs use a revolving fund where purchased development
rights are sold on the open market and the funds are reinvested in the purchase of new
development rights that will be banked. Communities that invest funds in areas other
than the purchase of development rights jeopardize their TDR program because only a
finite amount of money is available to purchase development rights.
However implemented, TDR programs must be designed to withstand legal
challenges. First, as discussed above, a market for development rights is critical. The
market will dictate whether a sending area is appropriate for down zoning or whether
such down zoning would leave no economically viable use for those property owners.
Designation of sending and receiving districts may also generate significant debate
(density in the sending areas is low, while density in the receiving areas is too high).
Next, zoning or the right to build in the receiving area should not be so restrictive so as to
force purchase of development rights for any type of development. Failure to allow some
use by right in the receiving district might be challenged as a taking.
162The Miami-Dade Board of County Commissioners adopted the East Everglades
Ordinance in 1981 that declares the Everglades an area of critical significance and
implements land use regulations that allow the transfer of development rights. The
programs is referred to as a severable use rights (SUR) program, because the right to
develop is “severed” from the sending property and transferred to a receiving property
more appropriate for development. The Miami-Dade County SUR program identifies
156
AMERICAN FARMLAND TRUST , supra note 30, at 128.157
PRUETZ, supra note 129, at 128.158
DANIELS, supra note 38, at 226.159
PRUETZ, supra note 129, at 128.160
Id.161
DANIELS, supra note 38, at 226.162
SALKIN, supra note 126, at § 56.04[3]; for further discussion of legal issues see Juergensmeyer, supranote 27, and Miller,
supra note 144.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
26
sending parcels within the East Everglades area and receiving parcels within the UDB.
The ratio for SURs varies from one SUR per five acres to one SUR per 40 acres.
The East Everglades Ordinance imposes strict environmental regulations within
the sending areas that include road standards and excavation limitations. As a result of
the environmental limitations and the density restrictions, landowners find it very
difficult and expensive to build in the East Everglades, providing incentives for them to
sell their development rights.
The receiving site may use the SURs to increase density, lot area, frontage, and
other development requirements on residential and commercial receiving sites in the
unincorporated parts of Miami-Dade County that are designated for urban development.
Sending zones are also eligible for a 10 percent reduction in the minimum lot size, a one
third reduction in the required front setback and an 18 percent increase in density.
Additional commercial floor area is allowed in commercial and office park zones.
Although initially of limited success, the success of the SUR program has
increased since 1995 because the Comprehensive Development Master Plan provides for
the use of SURs; the transfer ratios are high in certain areas; the ordinance has eighteen
different zones that can receive SURs; the administrative process is predictable and
uncomplicated; and the local government is supportive of the program. The Miami-Dade
County program is also successful because there is a substantial demand for additional
development in the area. Developers have found it cheaper to buy SURs than to buy
land. By the end of 1994, 213 SURs had been transferred to receiving sites.
1635. Florida Rural and Family Lands Protection Act
Passed by the Florida Legislature in 2001, the Rural and Family Lands Protection
Act (Act) allows the Department of Agriculture and Consumer Service (DACS) to protect
ranch and timber land by offering four options to willing land owners. DACS may:
·
Purchase traditional permanent conservation easements;·
Purchase less restrictive rural land protection easements;·
Purchase agricultural easements, which are 30 year restrictions on developmentand subdivision with an option for the government to buy the land; or
·
Pay farmers to improve wildlife habitat and water resources on their land under apermanent conservation easement.
While conservation easements are a familiar tool in Florida (see discussion above)
the Act is innovative in that it institutes options for varying degrees of restriction and
time parameters. It adds flexibility for both landowners and easement holders that was
not previously available. The Act is supported by the agricultural industry as a means to
keep family farms in business and realize value for their property while protecting the
property from subdivision and development.
While the Act passed in 2001, no funding has been set aside for the program. In
December of 2001, the DACS issued a legislative report that described the types of lands
163
PRUETZ, supra note 129, at 85.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
27
that would receive priority under the program. However, the 2002 and 2003 Legislatures
failed to allocate funds to the program. DACS had requested approximately $10 million
to fund the project. If future legislatures fund the program, this Act will significantly
impact local rural programs around the state, including Miami-Dade County. Funding
from the state- level can radically augment local efforts to preserve open space and rural
lands.
164D. Taxation Programs
The disparity between the market value of agricultural land for agriculture and for
other uses increases the pressure on farmers to sell their farms.
165 To reduce thetemptation or need to sell many states have enacted legislation giving real property tax
deferments, preferences, or exemptions to the owners of agricultural or eligible land.
Besides agriculture, eligible uses might be open space or timber production. Tax
programs can be effective when used in tandem with other mechanisms. Though tax
incentives do reduce the tax pressure, they do not always reduce the development
pressure, as the capital gains for land development may still outweigh the property tax
incentive in some markets.
166The purpose of agricultural tax programs is to help farmers stay in business by
reducing their real property taxes; to treat farmers fairly by taxing farmland based on its
value for agriculture instead of its value for development; and to protect farmland by
easing the financial pressures that force some farmers to sell their land.
167 Tax programsare beneficial because they correct inequities in the tax system created by development
pressures and they help farmers stay in business. Tax programs, unfortunately, cannot
ensure long term protection of farmland, and are criticized when they inadvertently
provide a subsidy to real estate speculators who keep their land in agriculture pending
development.
1681. Differential Assessment
Differential tax programs provide incentives for landowners to keep their land in
agriculture by assessing agricultural lands at its current or farm value rather than its fair
market value.
169 Agricultural value represents what farmers would pay to buy land inlight of the net farm income they can expect to receive from it. Full market value
represents what a willing buyer would pay for the land.
170 Every state except forMichigan has a differential assessment program. There are three kinds of differential
assessment programs: preferential assessment, deferred taxation, and restrictive
agreements.
Preferential assessment is the least restrictive of the three types because it does
not impose penalties for converting land to non-eligible uses. The agricultural value is
164
See Lancaster County, Pennsylvania, Task 2(c) Report.165
Id. at 285.166
Id.167
DANIELS, supra note 38, at 147.168
Id. at 151.169
FREILICH, supra note 29, at 285.170
DANIELS, supra note 38, at 147.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
28
multiplied by the local tax rate to determine the amount of real value tax due each year.
Farm buildings are generally taxed at their fair market value. These programs base
farmer’s tax bills on the agricultural value instead of the fair value as long as the lands
remain in agricultural use.
171The principle behind a deferred taxation program is that the tax on the market
value of the property is deferred until the property is developed. Deferred taxation
programs use the same process as preferential assessment programs to calculate property
taxes. The difference is that a tax is imposed on the landowner when the land is
converted to non-eligible uses or sold for development. Some states impose “rollback”
penalties that are calculated based on the sum of the tax benefits received, while other
states just require the landowner to pay a conversion tax.
172 Most states requirelandowners to renew their application for tax deferment each year.
The taxation programs are designed to target commercial agricultural land rather
than small farms used for recreation or land that is vacant pending development. To
achieve this goal landowners may be required to sign restrictive agreements (California)
or restrictive covenants (Georgia, Hawaii, New York and Pennsylvania). The restrictive
agreements must be signed as a condition precedent to the reassessment of the land for
agricultural purposes.
173 In Minnesota, this goal is achieved by having fairly restrictiveeligibility criteria whereby lots must be at least 10 acres, and meet an ownership and
production test. For the ownership test, the land must be the owner’s homestead or that
of a surviving spouse, child or sibling; the land must have been in possession of one of
the previously mentioned parties for seven years; or the land must be the homestead of a
shareholder in a family farm corporation. To be considered an eligible use the land must
be devoted to production of farm products for sale that provide at least 1/3 of the family’s
income, or yield at least $300 plus $10 per tillable acre in total income, including rent.
174The Florida Constitution provides for a differential assessment for agricultural
lands.
175 Whether or not land is considered agricultural land for tax assessment purposesdepends on the length of time the land has been utilized as agricultural land; the purchase
price paid; the size, as it relates to specific agricultural use; whether effort has been made
to care sufficiently and adequately for the land in accordance with accepted commercial
agricultural practices, including, without limitation, fertilizing, liming, tilling, mowing,
reforesting, and other accepted agricultural practices; whether such land is under lease
and, if so, the effective length, terms, and conditions of the lease; and such other factors
as may from time to time become applicable.
176 After land is qualified as agriculturalland, it is eligible for differential tax assessment.
2. Circuit Breaker Tax Relief Credits
Circuit breaker programs allow for farmers to take tax credits for part of their
local property tax bill. The cost of the tax credit is distributed among all the taxpayers in
171
Id. at 153.172
Id. at 154.173
FREILICH, supra note 29, at 286.174
DANIELS, supra note 38, at 154.175
FLA. CONST. ART 7 §4.176
FLA. STAT. CH. 193.461 (2002).Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
29
the state. A circuit breaker program depends on involvement at the state level. Only
Michigan, Wisconsin, New York and Iowa have instituted circuit breaker programs.
The New York program, adopted in 1996, provides farmers who earn at least 2/3
of their total household income from farming with relief from local school taxes levied on
agricultural land and buildings. Farmers receive a full credit for up to 250 acres of
farmland and a fifty percent credit for more than 250 acres. The amount of credit also
depends on a family’s income.
The other state programs operate similarly but also can require the farmer to sign
a restrictive agreement where the farmer promises not to build any non- farm structure for
ten years. In return, farmers are protected against taxes levied by local utilities and
receive credits against their state income taxes.
1773. Real Estate Transfer Taxes
Real estate transfer taxes are taxes on various property transactions such as the
transfer of property deeds and the transfer of a controlling ownership interest in entities
which own real property.
178 Many states, including Florida, charge the tax when a deedis recorded. State statutes generally spell out the conditions of the tax and for what
purposes the revenue may be used.
Real estate transfer taxes are frequently used for farmland preservation.
Maryland is the leading state using this type of tax through a ½ percent tax on the value
of all real estate transfers that is divided between parkland acquisition and farmland
protection.
179Florida’s real estate transfer tax, called the documentary stamp tax, is codified in
Chapter 201 of the Florida Statutes. The tax is primarily levied by the state and the
revenue is used for numerous purposes including the purchase of conservation lands
through Florida Forever and the Land Acquisition Trust Fund.
180 Counties may assessdocumentary stamp taxes in limited situations and only for the purpose of funding the
Housing Assistance Trust Fund.
181 Miami- Dade County is the only Florida county thathas imposed a documentary stamp tax.
182177
DANIELS, supra note 38, at 155-156.178
PETER M. FASS; MICHAEL E. SHAFF; DONALD B. ZIEF, REAL ESTATE INVESTMENT TRUSTS HANDBOOK§ 5:71 (2003).
179
AMERICAN FARMLAND TRUST, supra note 30, at 101; see also discussion of Montgomery County inTask 2(c).
180
FLA. STAT. CH. 201.15.181
FLA. STAT. CH. 201.031.182
MIAMI-DADE COUNTY ORDINANCES 29-7.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
30
E. Funding Programs
1. Impact Fees
Impact fees are mandatory payments paid by developers or builders in return for
development approval. They are calculated to be the proportionate share of the capital
cost (e.g. roads, schools, sewer lines, or gutters) created by a new development.
183 Thecharges are generally levied by local governments but are not taxes because impact fees
constitute a single payment, unlike periodic payments of taxes. The costs of developing
infrastructure for a new development are charged at the time of development, reducing
the need of the city or county to rely on bonds,
184 and the community is not forced to paythe high costs of development on the urban fringe or in other areas without existing
infrastructure. Impact fees exist in some form or another in every state in the nation.
185The power to charge impact fees is derived from local government’s police
powers. While some states enact enabling legislation for impact fees, others, such as
Florida, simply delegate the power to local governments through home rule power.
While local governments have limited powers to impose taxes, they have broad powers to
regulate in order to protect the health, safety and welfare of the community. Courts have
upheld the legality of impact fees if such fees meet the rationale nexus test, which ensures
a rational relationship between the demands of new development and assessments against
it.
186 There are two prongs to the rational nexus test. First there must be a need for anadditional public facility (i.e. schools, public safety, sewers) created by the new
development and the fee must not exceed the cost of providing the facility. Second, the
property charged the fee must derive a roughly proportional benefit from the new
facility.
187 Impact fees that do not meet this test may be considered takings, entitling theproperty owner to monetary damages.
Impact fee programs must be carefully designed so the fees are reasonable, and
fairly and accurately reflect a new development’s fair share of the necessary facility.
188Local governments often use careful economic analysis and planning to determine impact
fees. “The most widely implemented and judicially upheld impact fees are based on data
which indicate desired level-of-service standards for a particular facility and calculate the
cost of maintaining those standards in light of the increased demands created by new
development.”
189 While impact fees have not traditionally been used as a direct tool toprotect agricultural land, they have been used as part of an overall growth management
policy.
183
Frank, James E. & Paul B. Downing, Patterns of Impact Fee Use, in DEVELOPMENT IMPACT FEES 3(Arthur C. Nelson ed. 1988).
184
Id. at 4.185
James C. Nicholas, Julian C. Juergensmeyer & Ellen Margrethe Basse, Perspectives Concerning the Useof Environmental Mitigation Fees as Incentives in Environmental Protection (Part I),
7 ENVTL. LIABILITY25, 28 (1999).
186
See Id. at 30; Jordan v Village of Menomonee Falls, 137 N.W. 2d 442 (Wis. 1965).187
James C. Nicholas, supra note 185, at 37; see also Sarasota County v. Sarasota Church of Christ, Inc.,667 So.2d 180, 183 (Fla.1995).
188
Nicholas, supra note 185, at 30-1.189
Id. at 31.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
31
2. Environmental Mitigation Fees
A new type of impact fee is being proposed by environmental advocates called
environmental mitigation fees, one purpose of which may be agricultural preservation.
Environmental mitigation fees are a hybrid between impact fees and market based
environmental mitigation models. “The goal of environmental mitigation fees is to
harness market forces to make environmental protection profitable.”
190Traditionally, environmental pollution fees have been assessed on a case-by-case
basis.
191 Each individual development or polluting facility has been required to mitigateits own impact on its own site, or mitigate its impact through some regulatory means.
192The problem with this approach is that it may not meet comprehensive environmental
goals for the community because it is not based on a community wide plan.
An environmental mitigation fee requires long-range planning for environmental
goals. Agriculture and environmentally sensitive lands, critical habitat, endangered
species and other critical resources are identified early on. Then, the comprehensive plan
guides the assessment of impact of any development. “Government regulators would
determine the units of environmental impact associated with a new or existing project and
multiply the number of units by a price per unit.”
193 A developer would be charged basedon the formula and may choose (1) to pay and proceed with the project; (2) to reduce the
adverse impact and pay a reduced fee; or (3) to pay another firm to mitigate adverse
environmental impact elsewhere.
194 The money generated by the program could go intopreserving agricultural land through the purchase of development rights, a TDR program,
or other method discussed in this paper.
Although not a fee-based arrangement, in Miami-Dade, environmental impacts
are mitigated through regulatory mechanisms. Section 24-58 of the County Code
requires a permit for any development that alters County canal rights-of-way, mangrove
trees, tidal waters, submerged bay bottoms, wetlands, natural surface flows, or critical
groundwater sources. The environmental mitigation fee would be collected and used in
the protection of these same environmental resources.
3. Federal Programs
The United States Department of Agriculture (USDA) has a number of programs
to assist state and local governments and individual landowners with conservation. The
Food Security Act of 1985 created the Farmland Protection Program (FPP) which
provides funds to help purchase development rights to keep productive farmland in
agricultural uses.
195 This program was recently reauthorized and modified by the Farm190
James C. Nicholas, Julian C. Juergensmeyer & Ellen Margrethe Basse, Perspectives Concerning the Useof Environmental Mitigation Fees as Incentives in Environmental Protection (Part II),
7 ENVTL. LIABILITY69, 71 (1999).
191
Id.192
Id.193
Id.194
The third option might be similar to off site mitigation programs such as pollution trading and wetlandsmitigation programs. For more information see James C. Nicholas,
supra note 185.195
Pub. L. No. 99-198, 99 Stat. 354 (1985).Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
32
Security and Rural Investment Act of 2002.
196 The general purpose of the program is "toestablish and carry out a farmland protection program under which the Secretary shall
purchase conservation easements or other interests in eligible land… for the purpose of
protecting topsoil by limiting nonagricultural uses of the land."
197The program is administered through the Natural Resources Conservation Service
(NRCS), a division of the USDA. The NRCS provides technical and financial assistance
to state, tribal and local governments and non-governmental organizations that already
have farmland protection programs. Through the benefit of the FPP these governments
and organizations acquire easements and interests in land, while landowners agree to
develop and carry out a conservation plan on the land. A total of $30 million was
available in 2001 for the program.
States may cooperate with the federal government to devise creative funding
techniques for agricultural preservation. Martin County, Florida recently agreed to pay
for the speedy installation of water lines for a Superfund project that will bring clean
water to its residents. While a state’s portion of Superfund programs is usually only 10
percent, in exchange for Florida's payment of the full cost of the project, the federal
agency has agreed to give Florida a credit that can be used to offset the state's share of
future cleanups.
198 A similar program could be used for agricultural preservation or thefederal government might opt to give credit for farming programs as well as for clean up
programs.
F. Regulatory Techniques
1. Growth Tiers
Timing and sequencing deve lopment to coincide with the provision of public
facilities was first implemented in an innovative plan in Ramapo, New York and was
upheld by the courts in the landmark decision
Golden v. Planning Board of Town ofRamapo
.199 The basic idea is that all residential development must proceed in accordancewith the provision of adequate municipal facilities as established by a long-term
comprehensive and capital improvement program.
200 The importance of the Ramapoplan is the recognition of the fundamental constitutional principle that development on
the urban fringe can be controlled by linking the development with the planned extension
of capital improvements over a reasonable time.
A “tier” system utilizes the Ramapo principle by providing for the delineation of
functional areas within the region for the identification of goals and objectives and the
implementation of growth management techniques.
201 Generally five tiers are created.Tier I consists of the downtown area or urban core. Tier II consists of existing residential
areas within the urban area and older suburban areas. Tier III consists of the actively
196
Pub. L. No. 107-171, §2503, 116 Stat. 134, 267 (2002)197
Id. at 268.198
John Cushman Jr., Superfund Makes a Rare Deal with Florida, N.Y. TIMES, July 31, 2002, available athttp://www.nytimes.com/2002/07/31/politics/31SUPE.html
. (August 2, 2002).199
Golden v. Planning Board of Town of Ramapo, 334 N.Y.S. 2d 138 (N.Y. App. 1972).200
Freilich, supra note 5, at 34.201
Id. at 35.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
33
development area. Tier IV is the rural and agricultural land that is inappropriate or
premature for development. Tier V incorporates environmental and agricultural zones
that warrant preservation or protection.
202 The number of tiers varies according to thecurrent and desired land use pattern within the urban area, but will be similar to the
system described above.
2. Concurrency Programs
Concurrency programs tie development approvals to level of service (LOS)
standards. LOS standards measure the ratio of public facility capacity to the need for the
facility. Such a program takes into account all demand for the facilities, including
existing demand as well as the additional population added by new development
proposals. An adopted LOS standard reflects a policy decision concerning the
appropriate equilibrium between population and public facilities that may be applied to
new development in the standard setting and review process, and to the public capital
budgeting process. LOS standards conveniently provide a benchmark for monitoring the
growth management system.
203Florida was the first state to introduce “concurrency” requirements; the Florida
Statutes specifically provide that, “[P]ublic facilities and services needed to support
development shall be concurrent with the impacts of such development.”
204 Therequirement is part of Florida’s Growth Management Act of 1985 that was enacted to
discourage urban sprawl, improve existing infrastructure to support infill and
redevelopment, and to discourage urban development of rural lands.
205Concurrency programs do not concentrate on one particular sector of a city or
county; they look at a community comprehensively to plan for the entire area. The result
is that growth occurs at a rate that is economically beneficial to the community and in a
manner that retains land values. The specific techniques discussed above should be
implemented within the framework of the comprehensive plan.
Miami-Dade County has a Service Concurrency Management Program. No
development order shall be issued where LOS standards for all public facilities will not
meet or exceed LOS standards or where such an order would result in a reduction of
services, except in certain circumstances, such as when the development is located in a
designated urban infill area.
202
Id.203
S. Mark White, Adequate Public Facilities Ordinances and Transportation Management 8. PAS Report465 (1996).
204
West’s Fla. Sta. Ann. Section 163.3177 (10)(h).205
See generally West’s Fla. Sta. Ann. Section 163.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
34
3. Urban Service Boundaries
An urban service boundary (USB)
206 is a relatively simple technique forchanneling growth that involves designating an urban services area and a rural service
area. Planning studies designate the urban services areas, which are the most suitable to
the extension of municipal services such as streets, sewers, and water, and rural service
areas where development is restricted.
207 The municipality commits to providing urbanservices within the urban service area before going beyond it.
208 One of the mostimportant attributes of a USB is that it makes the development pattern predictable for
landowners and developers.
209There are generally four goals for a USB: (1) to make the most efficient use of
public tax money for infrastructure funding; (2) preservation of agricultural and
environmentally sensitive lands; (3) efficient provision of municipal services; and (4)
promotion of compact urban development.
210 The USB also preserves agricultural landvalues within the community.
The most challenging issue surrounding a USB is how and under what
circumstances the boundary should be moved.
211 The location of a USB significantlyimpacts how a community develops, and in the agricultural context, may determine what
agricultural land is given over to development and what land is preserved for farming.
Therefore, adjustments to a USB should only take place after deliberate planning
considerations, that take into account both urban and rural interests.
212 An effectiveboundary adjustment process should be “firm enough to provide predictability for longrange
planning, yet sufficiently flexible to respond to changed conditions.”
213 Somestates, such as Oregon, set out guidelines for adjusting boundaries. These guidelines
include compliance with a comprehensive plan, and the analysis of socio-economic
impacts on the community and the existence of intergovernmental agreements.
214Intergovernmental coordination is required to successfully implement a USB
program because most urban cores are associated with a municipality separate from the
unincorporated area of the county.
215 Intergovernmental agreements should define therole of each governmental entity involved and describe the process for boundary
adjustments.
Miami-Dade County’s Urban Development Boundary (UDB) is a USB. Details
of the Miami-Dade County UDB are provided above in Section II.
206
A USB is different from an urban growth boundary that identifies an urban core and designates certainuses appropriate. The focus is less on urban services than on uses such as siting of future development,
protection of natural lands and resources, and compact urban form.
See Smith, supra note 47 at 19.207
CALLIES, supra note 78, at 642.208
V. Gail Easley, Staying Inside the Lines 10 PAS Report 440 (1990).209
Smith, supra note 47, at 19.210
See Wash. St. Ann. § 36.70A. 110 (2003)211
Smith, supra note 47, at 20.212
Id. at 20.213
Easley, supra note 208, at 10.214
Id. at 4.215
Smith, supra note 47, at 21.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
35
IV. E
CONOMICS AND THE LAWA. Economic Value of Land
Preventing sprawl may be the most effective method of preserving the economic
value of land in Miami-Dade County. A 1995 Bank of America report stated, “Growth
has helped fuel … an unparalleled economic and population boom and has enabled
millions … to realize the enduring dream of home ownership … but sprawl has created
enormous costs… Ironically, unchecked sprawl has shifted from an engine of … growth
to a force that now threatens to inhibit growth and degrade the quality of our life.”
Indeed, the public infrastructure gap is nearing $4 trillion. Such high costs for
infrastructure impede development of community services and inhibit the preservation of
open space and agricultural lands. If urban growth consumes agricultural land, and
government money is spent building infrastructure, then community services and existing
infrastructure suffer. One conservative critic notes that more flexible zoning codes
“would allow for more innovative development designs that accomplish conservation
goals and satisfy consumer demand for housing alternatives. Ensuring that development
covers its infrastructure expenses will allow the marketplace to operate freely and
efficiently.”
216Preserving the economic value of land in Miami-Dade County can be
accomplished by concentrating on four goals:
1. Economic development through the preservation of agriculture;
2. Clustering of new development outside the urban area to reduce sprawl
and reduce infrastructure costs;
3. Maintain the character outside of the urban area; and
4. Develop strategies that are legally defensible.
B. Legal Framework
The following is intended to give a very general overview of the legal issues that
arise when local governments in Florida undertake planning and plan implementation.
Further legal analyses should be undertaken to address any specific program or ordinance
considered by the County for adoption.
The authority of local government agencies to adopt land use and zoning
regulations is derived from a state’s police power authority. Generally, comprehensive
growth management programs include police power regulations such as a zoning
ordinance incorporating density standards. Governments have the authority to regulate
the activity or use of property in order to protect or to prevent harm to the public health,
safety and welfare.
217 Though there are limitations on a government’s police power, the216
Samuel R. Staley & Matthew Hisrich, True Smart Growth, The Buckeye Institute Newsletter (May2002),
available at http://www.rppi.org/opeds/ohiosmartgrowth052102.pdf (August 2, 2002).217
See Keystone Bituminous Coal Assoc. v. DeBenedictis, 107 S.Ct. 1232 (1987); Euclid v. Ambler RealtyCo
., 272 U.S. 365 (1926); and Goldblatt v. Town of Hempstead, 369 U.S. 590 (1962).Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
36
courts have recognized the need for plans to deal with critical issues such as urban
sprawl, declining land values, environmental degradation, a lack of open space, and
agricultural preservation.
218Nonetheless, there are several types of legal issues that must be considered.
Generally, (1) does the local government have authority or police powers; (2) does the
action advance a legitimate governmental purpose; (3) is the system applied equally to
persons and land without operating in a discriminatory manner; (4) are the governmental
regulations implemented such that there is no "taking" of private property without "just
compensation"; and (5) do the government regulations afford substantive and procedural
due process to persons affected?
The authority of Florida’s local governments to plan is undisputed, and in fact
mandated, by Florida’s Growth Management Act of 1985. The other issues are
considered under three major headings: takings, impact fees/mitigation fees and due
process.
1. Takings
The majority of legal challenges to land use regulations fall under the claim that
the regulations constitute a "taking" of private property without "just compensation".
219If the purpose is to protect the public welfare, government may limit use of property
through regulation without a finding that a taking has occurred under the Fifth and
Fourteenth Amendments of the U.S. Constitution.
220 However, once a regulation221 hasbeen deemed to effectuate a taking, monetary compensation may be required to be paid
222or the regulation voided. If the regulation
223 does not involve a physical or title taking,but is in the nature of amenity protection such as open space preservation, environmental
protection, or agriculture preservation, the standard used is a balancing test to determine
whether the benefit to the public is outweighed by the burden to the land owner. The test
has two prongs: (1) does the regulation substantially advance a legitimate state interest,
and (2) does it deny an owner economically viable use of land.
224218
Robert H. Freilich & Jason M. Divelbiss, The Public Interest is Vindicated, 31 URBAN L. 731, 734(1999).
219
The following analysis involves a discussion of federal takings jurisprudence, which is applicable inboth federal courts and state courts in Florida.
220
Keystone Bituminous Coal Assoc., supra note 217.221
Since the seminal case Penn. C. Transp. Co. v. N. Y. C. Landmarks Commn., 438 U.S. 104 (1978), theUnited States Supreme Court has recognized three kinds of regulatory takings: physical, title, and
economic. A physical taking is one where a governmental entity invades private property regardless of the
extent of diminution in property value.
See Kaiser Aetna v. U. S., 444 U.S. 164 (1979). A title or exactiontaking does not involve land invasion, but results from the government accepting a title dedication or
monetary exaction representing a payment in lieu of dedication.
See Nollan v. Ca. Costal Commn, 483 U.S.825 (1987) and
Dolan v. City of Tigard, 512 U.S. 374 (1994). An economic taking is one where aregulation does not substantially advance legitimate state interest and denies an owner of economically
viable use of his land.
See Agins v. City of Tiburon, 447 U.S. 255 (1980).222
First English Evangelical Church v. County of L. A., 107 S.Ct. 2378 (1987).223
Nollan, supra note 221.224
See, e.g. Agins supra note 221; Haw. Hous. Auth. v. Midkiff, 467 U.S. 229 (1984); and Lucas v. S. C.Costal Council
, 505 U.S. 1003 (1992).Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
37
Under the first prong, the court will not construe the governmental action to be a
taking as long as the governmental entity has reasonably concluded that “the health,
safety, morals, or general welfare would be promoted by prohibiting a particular
contemplated use of land.”
225 The courts also require that the regulation is reasonablycalculated to meet the evil without exceeding the public necessity or substantially
affecting uses that do not “partake of the offensive character of those which create the
problem sought to be ameliorated.”
226 In short, the government must craft regulations in amanner that is rationally- related to the legitimate purpose it seeks to advance.
Under the second prong, a court must determine whether the property maintains
any permanent beneficial value when viewed as a whole.
227 Both federal and state courtshave uniformly held that all substantial use of property must be lost before an economic
taking occurs. Economic takings must be viewed in their entirety, and therefore a
diminution in value of even 99 percent has not been viewed as a taking.
228TDR programs have been particularly susceptible to takings claims, but if the
TDR system is designed appropriately it will be upheld. The key to a successful program
is effectively protecting the sending area's resources while offering the property owner
fair and reasonable compensation. Florida courts have upheld TDR programs in
City ofHollywood v. Hollywood, Inc
229 and Glisson v. Alachua County.230In the Hollywoodcase, the court upheld a city zoning ordinance that restricted beachfront lots to singlefamily
dwellings and granted the owner TDRs that could be applied to adjacent lots to
increase permissible density. The purpose of the ordinance was to preserve the
beachfront property, and the court dramatically noted, “Before us is the last unspoiled
beach area on the Gold Coast, a veritable Shangri-La in an otherwise endless Himalayan
mountain range of cement to the south.”
231 In Glisson, the court upheld a TDR programdesigned to protect threatened wetlands. In both cases, the court found that protecting
open space and environmentally sensitive areas was a legitimate state interest.
2. Impact Fees/ Mitigation Fees
Although there is no specific case law on mitigation fees in Florida, a review of
the impact fees jurisprudence is relevant because any mitigation fee legal analysis should
follow the same arguments. In 1994, the U.S. Supreme Court decided the important case
of
Dolan v. City of Tigard232 holding that not only must exactions have the requirednexus to a development’s impacts (a matter settled in
Nollan v. California CoastalCommission
,),233 but also that the degree of the exaction must be “roughly proportional to225
Penn C. Transp. Co., supra note 221, at 125.226
Kirsch Holding Co. v. Borough of Manasquan, 59 N.J. 241, 281 A.2d 513, 518 (1971).227
See, e.g. Concrete Pipe and Products, Inc. v. Constr. Laborers Pension Trust, 508 U.S. 602, 643-44(1993);
Pennel v. City of San Jose, 485 U.S. 1 (1988); Hodel v. Irving, 481 U.S. 704 (1987).228
Concrete Pipe and Products, supra note 227; see also City of Monterey v. Del Monte Dunes, 119 S.Ct.1624 (1999).
229
432 So. 2d 1332 (Fla. Dist. Ct. App. 1983), review denied, 441 So. 2d 632 (Fla. 1983).230
588 So. 2d 1030 (Fla. Dist. Ct. App. 1990), review denied, 570 So. 2d 1304 (Fla. 1990).231
Hollywood, supra note 229, at 1337-388.232
Dolan, supra note 221.233
Nollan, supra note 221.Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
38
the projected impact of the proposed development.”
234 Local governments mustdemonstrate that exactions imposed as a condition of development are not only related in
nature, but also in extent, to the impact of the development paying the fee.
The Florida Supreme Court has upheld local government’s authority to impose
impact fees based on general home rule and police power theories. The Growth
Management Act specifically encourages the use of impact fees,
235 and Florida courtshave adopted the rational nexus test as the appropriate standard by which to measure their
validity.
236 However, just as other land development regulations can only be exercisedwithin the bounds of substantive due process, so too are impact fee impositions similarly
bound. The Florida Supreme Court has adopted
237 and reaffirmed238 the dual rationalstandard as the appropriate measure of whether a local government has exceeded its
constitutional authority in the imposition of impact fees. Based on this case law, it is
likely that mitigation fees would be upheld in Miami-Dade County.
3. Due Process
Many land use claims are based on the due process clause of the Fourteenth
Amendment. Procedural due process is not discussed here as individuals cannot bring
these suits against a government for a legislative action. Substantive due process imposes
a requirement that the land use regulations must promote a legitimate public end in a
rationale manner.
239 Legitimate state interests are often described in zoning laws in termsof the protection or furtherance of the public health, safety, morals, or general welfare. A
landowner may assert that the regulation is arbitrary and capricious, bearing no
substantial relation to the public health, safety, morals, or general welfare, and is
therefore an invalid exercise of the police power (an “arbitrary and capricious due
process” or “substantive due process” claim).
240 This standard is a heavy burden for alandowner to overcome.
241V. M
IAMI-DADE COUNTY – VALUE PRESERVATION PRINCIPLEThe following analysis presents a guiding principle for analyzing how the County
might develop a program that will retain the value of agricultural land while
simultaneously protecting open space and rural areas for future generations. Although
the final recommendation (Task 2(d)) will be presented in light of the development
scenarios outlined in Task 1(f), the Team, based on the extensive input of the Citizens’
Advisory Committee, has determined that the final recommendation – the “preferred
development scenario – should set forth a means of protects open space in perpetuity in a
234
Dolan, supra note 221, at 388.235
See FLA. STAT. ch. 163.3202(3) (2001).236
Home Builders & Contract Assocn. of Palm Beach County, Inc. v. Board of County Commissioners,446 So.2d 140 (Fla. 4th DCA 1983).
237
Contractors & Builders Assocn., Inc. v. City of Dunedin, 329 So.2d 314 (1976).238
St. Johns County v. Northeast Florida Builders Assocn., Inc. 583, So.2d 635 (Fla. 1991)239
CALLIES, supra note 78, at 349.240
Eide v. Sarasota County, 908 F.2d 716, 722 (Fla. 1990); Euclid supra note 217, at 395.241
Restigouche v. Jupiter, 59 F.3d 1208, 1214 (11th Cir. 1995) (applying same rational relationship test asin equal protection cases).
Miami-Dade County Agriculture and Rural Area Study
Task 2(b)
doc.#55985;v.2/90685.001
39
manner that also protects the land investments made by property owners in the Study
Area. In order to meet the complex, and sometimes competing, goals of open space
preservation, a comprehensive program that includes any number of the agricultural
preservation techniques discussed in this paper - and more thoroughly in the Task 2(c)
report - may be employed. However, the Team recommends that the following principle
guide the ultimate recommendation:
Is there a regulatory balance that would provide a landowner a return on
his or her investment equal to or in excess of the reasonable return under
a suburban development alternative, while at the same time preserving
important open space and rural lands?
VI. C
ONCLUSIONThis Report is intended to inform the ongoing analysis being conducted by
the Citizens’ Advisory Committee and the various consultant Team members.
The background concepts set forth here will be refined in forthcoming reports and
analysis. Specifically, Task 2(c), “Analysis of Rural Land Uses,” describes how
five (5) communities from around the country have employed value-preservation
techniques – relying heavily on the concept of PDRs – to protect their threatened
agricultural economies and rural open space. In each case, these communities
have sought to protect the resource most critical to a viable agricultural economy
– the land. Furthermore, consistent with the guiding principle set forth in the
section above, each of these communities has done so by adopting funding
programs that ensure that the community at large, which benefits from the
preservation of this discrete area of the jurisdiction, shares in the burden of
agricultural preservation.
Abstract: Restoring the Urban Forest Ecosystem1
Mary L. Duryea, Eliana Kämpf Binelli, and Lawrence V. Korhnak, Editors
21. This document is the Abstract, Table of Contents, and Acknowledgments for SW-140, Restoring the Urban Forest Ecosystem, a CD-ROM (M.L. Duryea,
E. Kämpf Binelli, and L.V. Korhnak, Eds.) produced by the School of Forest Resources and Conservation, Florida Cooperative Extension Service,
Institute of Food and Agricultural Sciences, University of Florida. Publication date: June 2000. Please visit the EDIS Web site at http://edis.ifas.ufl.edu
2. Mary L. Duryea, Professor and Extension Forester, Eliana Kämpf Binelli, Extension Forester, and Lawrence V. Korhnak, Senior Biological Scientist,
School of Forest Resources and Conservation, Cooperative Extension Service, Institute of Food and Agricultural Sciences, University of Florida, PO Box
110410, Gainesville, FL 32611.
The Institute of Food and Agricultural Sciences is an equal opportunity/affirmative action employer authorized to provide research, educational
information and other services only to individuals and institutions that function without regard to race, color, sex, age, handicap, or national origin.
For information on obtaining other extension publications, contact your county Cooperative Extension Service office. Florida Cooperative
Extension Service/Institute of Food and Agricultural Sciences/University of Florida/Christine Taylor Waddill, Dean.
Restoring the Urban Forest
Ecosystem
The urban forest ecosystem can provide many
ecological services and benefits to cities and
communities including energy conservation,
contributing to global biodiversity, and maintaining
hydrologic and nutrient cycles. Yet in many
instances these benefits are not realized due to poor
health and management of the urban forest. Many
opportunities for restoration -- reestablishing the
structure and function of the urban forest ecosystem
-- exist. The goal of restoration is to return the urban
forest to a form which is more ecologically
sustainable. A restored urban forest will contribute
positively to the community instead of being a drain
on its resources. Many of our parks are composed of
trees and grass requiring intensive maintenance
inputs such as fertilizing, irrigating, mowing and
raking. With restoration these parks could take
advantage of natural processes such as nutrient and
water cycling, thereby saving money, energy and
resources for the community. Connecting these
restored parks to other ecosystems such as
waterways can also contribute to biodiversity and
wildlife conservation. Restoration sites can range
from backyards to neighborhoods to parks to whole
waterways and metropolitan areas. The United States
hosts an abundance of successful and innovative
urban forest restoration projects which illustrate the
potential for creativity, diversity and the ability to
tailor projects to local needs and opportunities. This
CD-ROM explains basic ecological principles for the
urban forest's water, soil, plant and animal
communities. It discusses problems common in the
urban forest such as aquatic eutrophication, soil
aeration, invasive plants and loss of biodiversity.
Solutions, strategies, examples, and additional
resources are presented to help make urban forest
restoration projects successful. Its goal is to inspire
the restoration of urban forest ecosystems which will,
in turn, restore and conserve our planet for future
generations.
Contents
Chapter 1: Restoring the Urban Forest
Ecosystem
- An Introduction - Mary L. DuryeaChapter 2: Basic Ecological Principles for
Restoration
- Mary L. Duryea, Eliana KämpfBinelli, and Henry L. Gholz
Abstract: Restoring the Urban Forest Ecosystem 2
Chapter 3: Biodiversity and the Restoration of the
Urban Forest Ecosystem
- Eliana Kämpf BinelliChapter 4: Plant Succession and Disturbances
in the Urban Forest Ecosystem
- Eliana KämpfBinelli, Henry L. Gholz, and Mary L. Duryea
Chapter 5: Developing a Restoration Plan
That Works
- William G. HubbardChapter 6: Restoring the Hydrological Cycle
in the Urban Forest Ecosystem
- Lawrence V.Korhnak
Chapter 7: Site Assessment and Soil
Improvement
- Kim D. CoderChapter 8: Enriching and Managing Urban
Forests for Wildlife
- Joseph M. SchaeferChapter 9: Invasive Plants and the
Restoration of the Urban Forest Ecosystem
-Hallie Dozier
Chapter 10: Glossary of Terms for Restoring
the Urban Forest Ecosystem
- Eliana KämpfBinelli, Mary L. Duryea, and Lawrence V. Korhnak
Acknowledgments
We are grateful for funding from the USDA
Forest Service, Cooperative Forestry through the
National Urban Community Forestry Advisory
Council's grants program. Special thanks to Suzanne
del Villar who patiently waited for all our reports.
We are also most grateful to Ed Macie, USDA Forest
Service, Region 8, Atlanta, who in addition to
supporting this CD-ROM has enthusiastically guided
and sponsored the Urban Forestry Institute for over
ten years.
At the University of Florida, we would like to
thank Wayne Smith for his continued encouragement
and support for this project. Also, many long hours
were spent by Howard Beck and Petraq Papajorgji of
IFAS Information Technologies they planned,
designed and successfully created this CD-ROM and
its printable version. They were assisted by Anna
Beck, Joe Bess and Rayna Elkins. Thank you all so
much.
We found many beautiful photos to describe
projects around the U.S. Everyone is credited with
each photo but we would like to extend our thanks to
all you photographers for your generosity in sharing
these beautiful scenes with us.
And finally, the authors also extend their sincere
gratitude to the many people around the U.S. who
shared information with us about their restoration
programs: Don Alam, Artesia, NM; Laurie Ames,
City of Seattle Dept. of Neighborhoods; Rob Buffler,
Greening the Great River Park, St. Paul, MN;
Charley Davis, Portland Parks and Recreation, OR;
Meridith Cornett, Minnesota Department of Natural
Resources; Sandy Diedrich, Forest Park Ivy Removal
Project, Portland, OR; Ray Emanuel, Drew Gardens,
NY, NY; Alice Ewen, American Forests,
Washington, DC; Steve Graham, City of Tampa
Parks Department, Tampa, FL; Steve Gubitti, Bill
Baggs Park Restoration, Department of
Environmental Protection, Tallahassee, FL; Paula
Hewitt, Open Road, NY, NY; Judy Okay, Difficult
Run Watershed Project, Virginia Department of
Forestry; Kit ONeill, Ravenna Creek Alliance,
Seattle, WA; John Rieger, Carmel Valley Restoration
and Enhancement Project, CA; Linda Robinson,
Naturescaping for Clean Rivers, Portland, OR; Joe
Schaefer, Schoolyard Ecosystems for Northeast
Florida, Gainesville, FL; Beth Stout, National
Wildlife Federation, Portland, OR; David M.
Wachtel, Chicago Wilderness; David J. Welsch,
USDA Forest Service, Northeastern Division,
Radnor, PA; Paul West, Seattle Dept. of Parks and
Recreation; and Greg Wolley, Metropolitan
Greenspaces, Metro, Portland, OR.
We dedicate this work to all the hard-working,
dedicated and creative people around the U.S. who
are finding so many ways to restore the beauty and
health to the urban forest ecosystem.
Chapter 1: Restoring the Urban Forest Ecosystem: An
Introduction1
Mary L. Duryea
21. This is Chapter 1 in SW-140, "Restoring the Urban Forest Ecosystem", a CD-ROM (M.L. Duryea, E. Kampf Binelli, and L.V. Korhnak, Eds.) produced by
the School of Forest Resources and Conservation, Florida Cooperative Extension Service, Institute of Food and Agricultural Sciences, University of
Florida. Publication date: June 2000. Please visit the EDIS Web site at http://edis.ifas.ufl.edu
2. Mary L. Duryea, Professor and Extension Forester, School of Resources and Conservation, Cooperative Extension Service, Institute of Food and
Agricultural Sciences, University of Florida, PO Box 110410, Gainesville, FL 32611
The Institute of Food and Agricultural Sciences is an equal opportunity/affirmative action employer authorized to provide research, educational
information and other services only to individuals and institutions that function without regard to race, color, sex, age, handicap, or national origin.
For information on obtaining other extension publications, contact your county Cooperative Extension Service office. Florida Cooperative
Extension Service/Institute of Food and Agricultural Sciences/University of Florida/Christine Taylor Waddill, Dean.
Abstract
Urban and community forests are often managed
as individual trees instead of whole forest
ecosystems. Cities inventory and manage these tree
species to meet many important needs such as energy
conservation, beauty, and recreation in the city. Yet,
there are many opportunities for urban forest
restoration to provide additional ecological benefits
such as storm-water management, wildlife
management, and biodiversity. Restoring the urban
forest ecosystem is reestablishing the ecological
health of the urban forest ecosystem. The goal of
restoration is to return the urban forest to a form
which is more ecologically sustainable for the
community; the restored urban forest will contribute
positively to the community instead of being a drain
on its resources. Many of our parks, for example, are
composed of trees and grass requiring intensive
maintenance inputs such as fertilizing, irrigating,
mowing and raking. With restoration these parks
could take advantage of natural processes such as
nutrient and water cycling, thereby saving money,
energy and resources for the community. Connecting
these restored parks to other ecosystems such as
waterways can also contribute to biodiversity and
wildlife management and conservation. The options
for restoration sites include: yards, vacant lots,
shopping centers, schoolyards, parks, industrial
parks, and waterways. The projects can be varied
such as: (1) The simple act of eliminating leaf-raking
in a park to reestablish the natural forest floor and the
natural cycling of nutrients; (2) The establishment of
understory plant species in a schoolyard to promote
wildlife; (3) The eradication of an invasive plant
species which is eliminating much of the understory
biodiversity in a park; (4) The re-design of a parking
lot to decrease stormwater runoff and provide a small
ecological wetland; or (5) The re-creation of a park
with species and ecosystems to be just the way it was
in the 1800s. The United States hosts an abundance
of successful and innovative urban forest restoration
projects. The two key ingredients that make these
projects so successful are the involvement of people
from the community and the formulation of a
restoration plan.
The Urban Forest Ecosystem
To define the urban forest ecosystem we take
the original definition of ecosystem and apply it to
the urban forest.
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 2
The urban forest ecosystem is a collection of
living organic matter (plants, animals, people,
insects, microbes, etc.) and dead organic matter
(lawn clippings, leaf-fall, branches) on a soil (with
all its urban characteristics) through which there is
cycling of chemicals and water and flow of energy.
When we think of the urban forest ecosystem we
can think of the whole city or community as one
ecosystem or we can focus in on a smaller parcel of
land as the urban forest ecosystem. The big picture,
bird's-eye-view is important to identify sites that
might need restoration (
Figure 1). For example, wemight see two parks that could be connected with a
greenway to benefit wildlife communities. Or we
might see an area of the city which is void of trees,
an urban heat island, that could be restored with a
tree canopy. Yet, we also need to look at the urban
forest ecosystem as smaller parcels of land such as
neighborhoods, parks, or schoolyards. At this level
we can see specific management alternatives and
specific ecological needs for each of these land units.
Figure 1.
When we think of the urban forest ecosystemwe can think of the whole city or community as one
ecosystem or we can focus in on a smaller parcel of land
(a park, schoolyard or industrial park, for example) as the
urban forest ecosystem. Photo by Hans Riekerk
What is "Restoring the Urban Forest
Ecosystem"?
Restoration has traditionally been defined as
reconstructing or repairing something, often a work
of art or ancient building. Ecologists have defined
ecological restoration to be:
• "The return of an ecosystem to a close
approximation of its condition prior to
disturbance." (National Research Council
1992)
• "The intentional alteration of a site to establish
a defined indigenous, historic ecosystem. The
goal of this process is to emulate the structure,
functioning, diversity and dynamics of the
specified ecosystem." (Society of Ecological
Restoration 1992)
• "Ecological restoration is the process of
renewing and maintaining ecosystem health."
(Society of Ecological Restoration 1995)
• "Ecological restoration is the process of
assisting the recovery and management of
ecological integrity. Ecological integrity
includes a critical range of variability in
biodiversity, ecological processes and structures,
regional and historical context, and sustainable
cultural practices. (Society of Ecological
Restoration 1996)
Most of these definitions center around the
recovery, repair or re-establishment of native
ecosystems. Because of the loss of species, the
increase in disturbances and several other factors,
exact restoration may be an impossible feat and
many people wish to call it rehabilitation.
Restoring the Urban Forest Ecosystem is
reestablishing the ecological health of the urban
forest ecosystem.
In urban forest ecosystems we have a very
different situation, and therefore we need to define
restoration differently. The urban forest is a mosaic
or patchwork of highly altered landscapes ranging
from street trees to neighborhoods with landscaping
to shopping centers to waterways to parks to
fragments of remaining native ecosystems. For this
CD-ROM and its series of publications we have
chosen to define restoration as reestablishing the
ecological health of the urban forest ecosystem.
More specifically, restoration means altering a site (a
park, waterway, neighborhood) to a state which is
more ecologically sustainable for the community or
city. Restoration might reestablish ecological
structure, functions, pathways, and/or cycles. A
restored site with its renewed or re-introduced
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 3
ecological attributes will contribute more positively
to the community instead of being a drain on its
resources.
Examples of potential sites and projects for
restoring the urban forest ecosystem include:
• The simple act of eliminating leaf-raking to
reestablish the natural forest floor and the
natural cycling of nutrients.
• The establishment of understory plant species
in a schoolyard to promote wildlife species.
• The eradication of an invasive plant species
which is eliminating much of the understory
biodiversity in a neighborhood.
• The clean-up of a vacant lot or site in a
neighborhood and the establishment of a park.
• The re-design of a parking lot to decrease
stormwater runoff and provide a small
ecological wetland.
• The re-creation of a park with the native
ecosystems that were present 100 years ago.
Potential sites for restoring the urban forest
ecosystem include (
Figures 2, 3, and 4):Figure 2.
A vacant or abandoned lot in an industrial areaof town.
Figure 3.
A small water-retention pond which could berestored with wetland species.
Figure 4.
A schoolyard.The Story of two parks
A description of two hypothetical parks offers
insights into the reasons and benefits of restoration.
Wilson Park
• Wilson Park has five baseball fields and four
basketball courts which are under constant use
by the community. (
Figure 5).• A monoculture of 60-year-old pine trees
surrounding the ball fields has swing sets and
picnic tables in its understory (
Figure 6). Lastyear when bark beetles invested loblolly pines in
nearby parks, plantations and natural areas, park
managers worried that they might lose this pine
forest to the beetle.
• When viewed closely we can see that not only
are there no understory plant species but the park
managers remove every leaf and twig that falls
to the ground (
Figure 7).• In another area of the park, managers work to
maintain a grass understory under several live
oaks (
Figure 8). With little light for grassgrowth, addition of fertilizers, water and
frequent mowing makes this an intensively
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 4
managed area for the park. Every leaf and
branch must also be removed in these hardwood
and grass forests.
Figure 5.
Wilson Park has several baseball fields and fourbasketball courts which are under constant use by the
community.
Figure 6.
A monoculture of 60-year-old pine treessurrounding the ball fields has swing sets and picnic tables
in its understory. Last year when bark beetles invested
loblolly pines in nearby parks, plantations, and natural
areas, park managers worried that they might lose this
pine forest to the beetle.
Figure 7.
When viewed closely we can see that not onlyare there no understory plant species but the park
managers remove every leaf and twig that falls to the
ground.
Figure 8.
In another area of the park, managers work tomaintain a grass understory under several live oaks. With
little light, addition of fertilizers, water and frequent mowing
makes this an intensively managed area for the park.
Every leaf and branch must also be removed in these
hardwood forests.
• A bird's-eye-view of another hardwood area
shows very little remaining on the ground
(
Figure 9). All leaves have been removed andthe resulting bare soil shows the exposed and
unprotected roots of shrubs and trees (
Figure10
).• This kind of management results in intensive
use of people and energy resources (
Figure 11).Often after the natural leaves and branches are
removed, landscape mulch is brought in to cover
the ground.
• One of the park managers has planted camelias
in one of the bare understories. Because these
are an exotic plant, maintenance of these flower
gardens has included additional fertilization and
installation of an irrigation system (
Figure 12).Andrews Park
• Andrews park has a natural creek running
through it (
Figure 13). The creek originatesoutside the town, and so the park provides a way
to connect several ecosystems as it meanders
through the park and town.
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 5
Figure 9.
A bird's-eye-view of another hardwood area inthe park shows very little remaining on the ground.
Figure 10.
All leaves have been removed and the resultingbare soil shows the exposed and unprotected roots of
shrubs and trees.
Figure 11.
This kind of management results in intensiveuse of people and energy resources.
Figure 12.
One of the park managers has plantedcamelias in one of the bare understories. Because these
are an exotic plant, maintenance of these flower gardens
has included additional fertilization and installation of an
irrigation system. Photo by Larry Korhnak
• Several ponds and other wetland areas support
habitat for wildlife in the park (
Figure 14).• A walkway across one of the wetland areas
offers entry and a look at this wetland ecosystem
(
Figure 15).• Fallen leaves and branches maintain a natural
mulch for the park (
Figure 16).• Playground areas are well-defined as are the
special areas where plant life is being restored
(
Figure 17)• Fallen logs are left lying next to hiking trails
and on the forest floor to enhance natural decay
and nutrient cycling (
Figure 18).• Signs are utilized to educate people about the
park's ecosystems (
Figure 19).Developing a Checklist
It's good to look thoughtfully and critically at
our parks, neighborhoods, waterways and other
urban forests to see how they contribute ecologically
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 6
Figure 13.
Andrews park has a natural creek runningthrough it. Photo by Larry Korhnak
Figure 14.
Several ponds and other wetland areassupport habitat for wildlife in the park. Photo by Larry
Korhnak
Figure 15.
A walkway across one of the wetland areasoffers entry and a look at this ecosystem. Photo by Larry
Korhnak
Figure 16.
Fallen leaves and branches maintain a naturalmulch for the park helping to sustain the nutrient cycle in
the ecosystem. Photo by Larry Korhnak
Figure 17.
Playground areas are well-defined as are thespecial areas where plant life is being restored.
to the community. These benefits can be utilized to
gain support for restoration projects. By using a
checklist we can estimate the benefits for any area
within the urban forest ecosystem.
A Checklist of Wilson and Andrews Parks
shows the contrasting ecological benefits of the two
parks (
Figure 20).Both parks contribute recreational benefits to
the community. The monoculture of loblolly pines
and the hardwood forests at Wilson Park provide
very little biodiversity compared to the natural
ecosystems with many structural layers and plants at
Andrews Park. Parking lots and forests with very
little understory vegetation and natural mulch result
in high levels of stormwater runoff at Wilson Park.
The creek and wetland areas along with the forest
floor with its high water infiltration rates offer
several ways to dispose of stormwater at Andrews
Park. Andrews is a low maintenance, low energy-use
park compared to the high energy levels to maintain
Wilson Park. The removal of all leaves, twigs, and
fallen logs at Wilson Park means that nutrients are
being removed from the site annually; this will
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 7
Figure 18.
Fallen logs are left lying next to hiking trails andon the forest floor to enhance natural decay and nutrient
cycling. Photo by Eliana Kampf Binelli
Figure 19.
Signs are utilized to educate people about thepark's ecosystems. Photo by Larry Korhnak
Figure 20.
By using a checklist we can estimate thebenefits for any area within the urban forest ecosystem.
This checklist compares the ecological benefits of Wilson
and Andrews parks.
contribute to impoverishment of the site over time.
In addition, organic matter will not be present in the
soil to aid in water and nutrient retention. This
interruption of the natural nutrient cycle can be
remedied easily by retaining fallen plant materials as
in Andrews Park.
And finally, the Socio-Economic category of
benefits. Parks, greenways and natural areas
contribute to the economic health of a community.
For example, before the construction of the Pinellas
Trail (greenway), the city of Dunedin, FL had a 50%
occupancy rate and now with the new greenway,
there are no vacancies (Department of
Environmental Protection 1996). People come or
stay to recreate in communities; wildlife watching
alone generates $18.1 billion in the nation (Caudill
1997). Real estate prices are enhanced with the
presence of natural areas, parks and trees. The
improved psychological well-being of the citizens in
a community or neighborhood with parks and trees
has also been documented (Schroeder and Lewis
1991). People viewing trees have slower heartbeats,
lower blood pressure, and more relaxed brain wave
patterns than people viewing urban areas without
vegetation (Ulrich 1981).
It can be very advantageous to quantify costs
and benefits for maintaining or restoring areas. In
addition to stormwater and energy conservation cost
reductions, other less tangible benefits such as health
and recreation can be demonstrated. Recreational
studies have shown that citizens often prefer
recreating in parks near their homes, emphasizing the
importance of community parks (Schroeder 1990).
In Chicago, 50% of all the people visiting forest
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 8
preserves traveled 10 minutes or less from their
homes (Young and Flowers 1982). In 1996, 2.7
million Floridians participated in wildlife
recreational activities within a mile of their homes
(Florida Game and Fresh Water Fish Commission
1998). It is very important for urban foresters to
demonstrate to their city councils and managing
agencies the importance of parks and trees as
infrastructure in their communities.
Where can We Restore?
The options for restoration sites and projects in
cities and communities are endless. Here are a few:
• Yards can be enhanced with native species or
even native ecosystems (
Figure 21).• Vacant lots, often ignored or treated poorly for
many years, are often candidates for restoration.
• The possibilities for better energy conservation
and stormwater management in shopping center
parking lots are great (
Figure 22).• Street trees, aging or lacking diversity, can be
restored.
• Schoolyards can become natural areas with
unlimited potential as educational areas.
• Industrials parks can be transformed.
• Waterways can be enhanced and connected to
support recreational and hydrological benefits
(
Figure 23).Figure 21.
Yards can be enhanced with native species oreven native ecosystems. Instead of a typical
mono-species hedge or a fence, this area between two
neighbors has been restored and planted with native
species.
Figure 22.
The possibilities for better energy conservationand stormwater management in shopping center parking
lots are great.
Figure 23.
Waterways such as this creek can beenhanced with native species and connected to support
recreational and hydrological benefits.
Examples of Sucessful Projects
One objective of this CD-ROM was to find and
showcase successful restoration projects in the U.S.
We have been overwhelmed with the variety and the
high quality of projects being implemented
throughout our cities and communities. There is a
tremendous amount of creativity, ingenuity, and hard
work going into these projects. The high quality and
success are due to the amount of effort by so many
talented people ranging from young children to
funding agency personnel to natural resource
managers and community development
professionals. Partnerships are a common ingredient
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 9
of these projects. As you can see the variety
illustrates the imagination involved and the potential
for even more new projects in other communities.
The Forest Park Ivy Removal Project in
Portland
Sandy Diedrich saw a problem in her
neighborhood park and decided to take the lead in
trying to remedy it. Forest Park, is a 5,000 acre urban
park in Portland, Oregon -- one of the largest urban
forested parks in the country. It has 70 miles of trails
and 30 miles of creeks and tributaries. But it also has
English ivy, a common landscaping plant, which has
invaded the park, covering the native understory
plants and trees, and reducing the biodiversity in the
forest. Controlling the ivy is a challenge - because it
is so mixed with the native plants, herbicides are not
feasible. Instead manual control is necessary (
Figure24
). In 1993, Sandy started a program withvolunteers, specifically with high school students
(
Figure 25). She developed workshops andworkdays when citizens would come to help. In
addition to eradicating the ivy in the park, the
workshops taught nearby residents methods for ivy
control in their yards - the source of the ivy in the
park (
Figure 26). Through their work with thisproject, the high school students learned about the
basic ecology of the park, working together as a
team, and the importance of environmental projects
in the community. Alex Johnson, a high school
student and crew leader, noted that, "It's a chance to
make a difference. I've never known about the forest
and here I've learned a lot about nature."
Figure 24.
Crew leaders demonstrate ivy removalmethods.
Figure 25.
Sandy Driedrich (center) with the crew leaders(Bruno Precciozzi, Kristin Harman, Alex Johnson, and
Heidi Dragoo) in the headquarters of the Forest Park Ivy
Removal Project.
Figure 26.
Standing in front of an area where ivy has beenremoved and the forest's natural biodiversity is returning.
Drew Gardens in New York
Ray Emanuel and several others in the Bronx,
New York identified a site in their community that
had potential to be restored. The site was a vacant lot
located next to a school; for years this lot was used
for dumping and even criminal activities. Their goal
was to transform the space into a park for the
community and the school children. This
community-driven initiative including corporations,
the Urban Resources Partnership, and the community
began with planning and clean-up of the site. Fall
clean-ups and spring festivals involve the community
and corporate volunteers. High school students work
at the gardens and this work program is part of a job
protocol educational program (
Figure 27). Severalhigh school classes utilize the gardens for their
instruction including art, language arts (especially
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 10
writing), and science classes. Ecology Days at the
gardens include stations where participants can learn
about subjects such as water testing of the Bronx
River, composting, small wildlife, and edible wild
plants (
Figure 28).Figure 27.
A vacant lot located next to a school in NewYork was transformed into a park for the community and
the school children.
Figure 28.
Included in this new park, named DrewGardens, are trails and a deck to view the Bronx River.
Apex Park in Tampa
Apex Park is on Davis Island, a small island in
Tampa. It is the first thing you see after you cross the
bridge to the island. And the residents wanted the
first impression to be the best. So they approached
Steve Graham, Tampa's urban forester for assistance
in restoring the site, a small piece of land about an
acre in size. After researching old photos and
documents and some remnant ecosystems in the area,
they arrived at a list of plants that would have made
up the ecosystem before development of the island
(
Figure 29). They were delighted to find one grass,twisted fiddle leaf, that was endangered and found
some specimens still remaining on the island (
Figure30
). They planted a small area with native tree andshrub species including twisted fiddleleaf. The other
small part of the park was landscaped with grass to
showcase and allow viewing of the native ecosystem
(
Figure 31). The park has kindled interest amongresidents in native species and several people have
landscaped their yards with many of these species.
Figure 29.
With the help of Steve Graham, Tampa's urbanforester, the community of Davis Island restored native
plants at Apex Park.
Figure 30.
One plant, twisted fiddleleaf, was endangeredso the community collected specimens and planted it at
the park.
Landscaping for Wildlife
An educational program developed by the
Florida Cooperative Extension Service has given
homeowners the knowledge and tools for
landscaping their backyards and small urban lots for
wildlife using ecological principles (
Figure 32).Workshops are aided by the inclusion of a
participant's guide, instructor's guide and videos
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 11
Figure 31.
The other part of the park was landscaped withgrass to showcase and allow viewing of the native
ecosystem.
developed by extension specialists. The first of three
modules entitled "Landscaping for Wildlife:
Providing Food in Your Yard" demonstrates how to
restore a remnant of native landscape, start a
bird-feeding program, control squirrels, plant a wild
bird food plot, and feed hummingbirds and
butterflies. The second module enables participants
to select plants to provide good wildlife cover
including bird and bat houses, burrows for toads and
other small mammals, treefrog houses, rock piles for
lizards and snakes and brush piles for birds and
rabbits
(Figure 33). The third module highlights theimportance of the third wildlife requirement - water.
Figure 32.
In the Landscaping for Wildlife program,homeowners learn how to enhance wildlife habitat in their
backyards. Photo by Joe Schaefer
Figure 33.
The second module enables participants toselect plants to provide good wildlife cover including bird
and bat houses, burrows for toads and other small
mammals, treefrog houses, rock piles for lizards and
snakes and brush piles for birds and rabbits. Photo by Joe
Schaefer
Naturescaping For Clean Rivers
Landscaping your backyard can have a positive
impact on the environment. That's the theme for
Portland's Naturescaping For Clean Rivers project
(
Figures 34 and 35). "Rainwater runoff, orstormwater, becomes a problem in urban areas
because of the thousands of acres of impervious
surface: roofs, roads, driveways, and parking lots,"
notes the project workbook. This runoff contains
contaminants such as oils, metals, and chemicals.
The goal of naturescaping is to improve the quality
and reduce the quantity of water reaching storm
drains. Workshops teach homeowners how to
landscape with native plants which require much less
water, fertilizers, mowing, and chemicals to maintain
(
Figures 36 and 37). Other classes includecomposting, attracting wildlife and reducing
pesticide use. Neighbors work together to host
workshops in their communities; all workshop
participants receive project workbooks which help
them develop an action plan for their yard.
Restoring Fire In Haile Plantation
A neighborhood in Gainesville, Florida wanted
to restore the native longleaf pine ecosystem as well
as reduce the fire hazard for their homes. In the past,
fire was a natural disturbance in Florida longleaf pine
ecosystems. Yet, development as well as new forest
practices have excluded fire from many of Florida's
ecosystems. The neighborhood decided to re-instate
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 12
Figure 34.
In the Naturescaping for Clean Rivers programhomeowners learn how to landscape with native plants
which require much less water, fertilizers, mowing, and
chemicals to maintain. Here a backyard is prepared for
planting. Photo by Linda Robinson
Figure 35.
The backyard is transformed into an energyand water efficient native landscape. Photo by Linda
Robinson
Figure 36.
Native wildflowers adorn a "naturescaped"backyard. Photo by Linda Robinson
Figure 37.
Butterfly gardens are a popular part of theNaturescaping program. Photo by Linda Robinson
this natural ecological process to the small patches of
forest in their community (
Figure 38). Fires reducethe competing hardwoods allowing longleaf pine to
regenerate and become reestablished in the
ecosystem (
Figure 39). Educational signs are a bigpart of the program.
Figure 38.
A neighborhood in Gainesville, Florida hasbrought fire in as a management tool to restore the native
longleaf pine ecosystem as well as reduce the fire hazard
for their homes. Photo by Eliana Kampf Binelli
Greening the Great River Park
The Mississippi River, as with most rivers in the
world, became a center of industry and shipping as
St. Paul, Minnesota became a prosperous city. But
often as with most industrial areas the native forests
along the river were destroyed and replaced with
industrial buildings, pavement, and warehouses. The
Greening the Great River Park Program, established
in 1995, seeks to restore many of these areas along
the River (
Figures 40 and 41). This public-privatepartnership includes The Saint Paul Foundation, City
of St. Paul and others including thousands of
volunteer and over 240 partner organizations. The
project involves the landscaping of over 100 private
industrial lands with the four native plant ecosystems
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 13
Figure 39.
Fires reduce the competing hardwoodsallowing longleaf pine to regenerate and become
reestablished in the ecosystem.
including 30,000 trees and shrubs that occupied the
area in the past. "Our goal is to have a 50% canopy
cover throughout the valley. In 20 to 25 years, as the
trees reach mature heights, we want the valley to
look as though the buildings were placed in a forest
rather than some trees were planted around
buildings."
Figure 40.
The Greening the Great River Park Program,established in 1995, seeks to restore many sites in
industrial areas along the River. This shows an industrial
site before restoration. Photo by Rob Buffler
Figure 41.
Over 100 private industrial lands have beenlandscaped and planted with four native plant
ecosystems. This shows the same site after restoration.
Photo by Rob Buffler
A Community Park in New York City
A one-acre lot used as a bus garage for many
years and next to three schools was the site for the
birth of a community park in New York City. The
planning began in 1990 with meetings involving the
whole community - city agencies, non-profit
organizations (headed by "Open Road"), students,
businesses, neighbors and more. The grass-roots
park design includes a greenhouse, basketball area,
nature pond with plantings, wildlife area, and
playground (
Figures 42). To restore this "brownfield" site the area needed to be lined with plastic and
new soil needed to be imported. However, the group
including professional engineers and school children,
decided to develop a composting system and produce
compost from nearby businesses to produce the
"soil." The newly invented composting system is
now sought by many other communities in New
York. School classes using the park range from
science and gardening to energy and physics to
poetry and art. A math class, for example, helped
design the greenhouse. Paula Hewitt, the project
creator and Open Road Director, emphasizes that
"the purpose of the park is to be educational, yet we
have a very relaxed, fun atmosphere" (
Figures 43and 44
). The park is open to the community everyday of the year.
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 14
Figure 42.
The planning for this community park in NewYork City began in 1990 with meetings involving the whole
community - city agencies, non-profit organizations
(headed by "Open Road"), students, businesses,
neighbors and more. The grass-roots park design
includes a greenhouse, basketball area, nature pond with
plantings, wildlife area, and playground.
Figure 43.
Paula Hewitt, the community organizer, looksfor turtles and fish in the park's pond with neighborhood
kids.
Figure 44.
Gerald Brinson, who started as a volunteer forthe park and is now part of the staff, describes the new
dock project with flowing water that he is constructing.
Bill Baggs Park
In 1991 Hurricane Andrew struck Miami and its
surrounding communities including Key Biscayne.
Bill Baggs Park which until that time was mostly
occupied with an invasive tree, Australian pine, was
completely destroyed (
Figure 45).Figure 45.
In 1991 when Hurricane Andrew struck southFlorida, the non-native Australian pine forest at Bill Baggs
Park on Key Biscayne was completely destroyed.
The nearly clean slate provided an opportunity
and several visionaries saw that it was a possible
chance to restore the park. With partnering between
federal, state, county, city and many non-profit
groups, a proposal and plan was developed to
re-create the park to the way it was 100 years ago.
They researched the five native ecosystems including
four wetland areas that had occupied the site
(
Figures 46 and 47).Historical and recreational amenities were also
considered - for example, without the shade of the
previous forest, nine picnic shelters needed to be
constructed (
Figure 48). Cultural history includingarchaeological findings were incorporated into the
plan (
Figure 49). The ecosystems were restored andfuture invasions of non-native plants were monitored
by volunteers. Educational displays were important
to inform the public about the process of restoration
as well as the diversity of the "new" ecosystems
(
Figures 50 and 51).Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 15
Figure 46.
With partnering between federal, state, county,city and many non-profit groups, a restoration proposal
and plan was developed to restore the park with the five
native ecosystems that it had 100 years ago. Old
documents were studied to carefully re-create and map
the ecosystems.
Figure 47.
The coastal strand ecosystem three years afterplanting shows the restoration success.
Figure 48.
The shade that had been removed with theAustralian pine tree canopy had to be replaced with
several picnic shelters.
Figure 49.
The historical, cultural, and archaelogicalsignificance of the site such as this 1825 lighthouse with
restored lighthouse-keeper's house was an important part
of the restoration plan.
Figure 50.
Involving the park's neighbors and thecommunity in all the stages was very important to the
restoration success. Nearby condominiums can be seen
from the restored south Florida slash pine ecosystem.
Streamside Restoration in Virginia
The Difficult Run Watershed in Virginia has
over one-half million acres of forests and urban
communities. Nonpoint source pollution is affecting
the water quality of the Difficult Run River and
downstream the Potomac River and Chesapeake
Bay. This restoration project is a partnership with
the Virginia Department of Forestry, Environmental
Protection Agency, Virginia Department of
Conservation and Recreation, Chesapeake Bay
Foundation and the USDA Forest Service. Together
they are striving to:
• Improve water quality by enhancing and
restoring streamside forests.
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 16
Figure 51.
Educational displays were important to informthe public about the process of restoration as well as the
diversity of the "new" ecosystems such as the mangroves
along the ocean and bay.
• Increase public awareness and education
regarding the value of riparian forests.
• Improve fish and wildlife habitat (
Figure 52).Over 8,000 trees have been planted to reestablish
riparian buffers or streamside forests to restore and
maintain this important watershed.
Figure 52.
The Difficult Run Watershed Project restoresstreamside forests which act as buffers to protect water
quality and fish and wildlife habitat in riparian ecosystems.
Photo by Judy Okay
The Two Key Ingredients
These projects have been very successful
because they all had two key ingredients. First, the
people. All projects became an essential part of the
community because they involved the people in the
community from the start and then in every step.
People included all stakeholders such as citizens (all
ages), businesses, non-profit groups, volunteers, and
government agencies. Collectively these people put
together the second key ingredient to success - a
plan. As you will see in Chapter 5, the successful
restoration plan contains a vision, goal, objectives,
action plans and evaluation tools. Well-developed
plans demonstrate the need for the project and are
used to seek public and financial support. These
plans are usually very effective at obtaining funding
and other in-kind support. Successful projects have
support of the people and a well laid-out plan (
Figure53
).Figure 53.
Successful restoration projects have two keyingredients - support of the people and a well laid-out plan.
Conclusions
There are many options for restoring ecological
benefits in your community. It is important to
consider the whole city or community as an
ecosystem and then to focus in on parcels or projects
that could benefit that ecosystem or landscape as a
whole. Restoration projects can be as small as
Chapter 1: Restoring the Urban Forest Ecosystem: An Introduction 17
backyards to parking lots, city streets, parks,
waterways and any place where there are or could be
trees. Most often it's important to start with a small
manageable project. The United States hosts an
abundance of successful and innovative urban forest
restoration projects. The Bronx's Drew Park brought
life back to a vacant lot next to a school. Portland's
Ivy Project removed invasive ivy at the 5,000 acre
Forest Park. Greening the Great Green River is
restoring industrial parks along the Mississippi
River. The possibilities for restoration projects are
unlimited and up to the imagination and energy of
people (
Figure 54). Planning and involving thecommunity - the stakeholders - are the two most
important ingredients for success.
Figure 54.
The possibilities for restoration projects areunlimited and up to the imagination and energy of people.
Literature Cited
Caudill, A. 1997. 1991 National impacts of non
consumptive wildlife related recreation. Div. of
Economics. US Fish and Wildlife Service.
Arlington. 8 p.
National Research Council. 1992. Restoration
of aquatic ecosystems: science, technology, and
public policy. Committee on Restoration of Aquatic
Ecosystems - Science, Technology and Public Policy,
Water Science and Technology Board, Commission
on Geosciences, Environment, and Resources.
National Academy Press. Washington, D.C. 552 p.
Florida Department of Environmental
Protection. 1996. Environmental Benefits of
Greenways Summary Sheet. 2 p.
Schroeder, H. 1990. Perceptions and
preferences of urban forest users. Journal of
Arboriculture 16(3):58-61.
Schroeder, H. and C. Lewis. 1991.
Psychological benefits and costs of urban forests.
Pages 66-68 In: Proceedings of the Fifth National
Urban Forest Conference. Los Angeles, CA.
Ulrich, R.S. 1981. Natural versus urban scenes:
Some psychophysiological effects. Environment and
Behavior. 13:523-556.
Young, R.A. and M.L. Flowers. 1982. Users of
an urban natural area: their characteristics, use
patterns, satisfactions, and recommendations.
University of Illinois, Department of Forestry,
Forestry Research Report 82-4.
Chapter 2: Basic Ecological Principles for Restoration1
Mary L. Duryea, Eliana Kämpf Binelli, and Henry L. Gholz
21. This is Chapter 2 in SW-140, "Restoring the Urban Forest Ecosystem", a CD-ROM (M.L. Duryea, E. Kampf Binelli, and L.V. Korhnak, Eds.) produced by
the School of Forest Resources and Conservation, Florida Cooperative Extension Service, Institute of Food and Agricultural Sciences, University of
Florida. Publication date: June 2000. Please visit the EDIS Web site at http://edis.ifas.ufl.edu
2. Mary L. Duryea, Professor and Extension Forester, Eliana Kämpf Binelli, Extension Forester, and Henry L. Gholz, Professor, School of Forest Resources
and Conservation, Institute of Food and Agricultural Sciences, University of Florida, PO Box 110410, Gainesville, FL 32611
The Institute of Food and Agricultural Sciences is an equal opportunity/affirmative action employer authorized to provide research, educational
information and other services only to individuals and institutions that function without regard to race, color, sex, age, handicap, or national origin.
For information on obtaining other extension publications, contact your county Cooperative Extension Service office. Florida Cooperative
Extension Service/Institute of Food and Agricultural Sciences/University of Florida/Christine Taylor Waddill, Dean.
Abstract
Traditionally the urban forest has been viewed
as trees in the city - often along streets and in small
groups in other public places such as parks.
However, another way to look at the urban forest is
as an ecosystem, including many more living
components than trees (people, shrubs, herbs,
animals, microorganisms), a physical environment
(light, moisture, soil, rocks), energy flow from the
sun and water and nutrient cycles. A first step in
reorienting our view of urban forests and their
management is to review some important ecological
principles and to see how they apply to restoration
and management. The goal of this chapter is to
examine urban forests as ecosystems and to discuss
some of the opportunities for managing urban forest
ecosystems to provide more natural benefits to
communities and cities. By comparing the present
state of the urban forest ecosystem (UFE) to natural
ecosystems, we can learn how to manage the UFE for
some of the natural benefits it can provide. These
include energy conservation, stormwater
management, wildlife conservation, and recycling or
solid waste management. The urban forest
ecosystem is an open system with energy and
materials constantly entering and leaving the system.
Producers (mainly green plants) and consumers
(organisms dependent on living and dead plant and
animal matter) make up the living portion of all
ecosystems which are linked together in complex
networks called food webs. Cities are largely
consumers relying on production of food, energy and
natural resource from outer agricultural, forested and
other natural areas. The urban forest ecosystem can
provide many opportunities for ameliorating the
drain and stress on our natural resources. For
example, by cooling the city with a forest canopy, we
are less dependent on outside natural resources for
air conditioning. By providing natural areas for
water infiltration, storage and evaporation of
rainwater, the waste water from our streets and other
impervious surfaces is reduced. When leaves,
branches, and grass-clippings are left on-site instead
of being removed, these natural materials sustain the
natural nutrient cycle and provide the same benefits
that we ascribe to mulches in gardens and landscapes.
Urban forests can also help reduce atmospheric CO
2build-up in two ways by reducing fossil fuel (energy)
use and by increasing carbon storage. Finally, the
UFE can provide wildlife habitat and help with the
movement and conservation of some organisms
through connectivity. Seven guidelines to restore and
manage the urban forest ecosystem are: (1) Restore
and manage the UFE to decrease consumption and
contribute to conservation; (2) Restore and manage
Chapter 2: Basic Ecological Principles for Restoration 2
the UFE for its water cycling benefits; (3) Restore
and manage the nutrient cycle within the UFE:; (4)
Restore and manage the UFE to support greater
biodiversity; (5) Restore natural forest ecosystems in
the city; (6) Educate policy makers, city managers
and the public about the benefits of a healthy UFE;
and (7) Incorporate UFE management and
restoration into urban and regional planning.
Introduction
Traditionally the urban forest has been viewed
as trees in the city - often along streets and in small
groups in other public places such as parks
(Figure1)
. Managing these trees has included inventoryingthe tree population and assessing their health. We
have cultured and managed them mostly as
individuals, and this is called arboriculture.
However, another way to look at urban forests is as
ecosystems, with many more components (people,
animals, microorganisms), a physical environment
(sidewalks, soil, rocks), energy flow (sun) and
processes (water, nutrient cycles)
(Figure 2). Thisecological perspective is more comprehensive,
incorporating biological, physical, chemical and
social components. This approach offers a great
opportunity to enhance the environmental benefits of
forests in urban areas. The environmental benefits
gained from a healthy urban forest ecosystem (UFE)
include energy savings, reduction of waste and
stormwater costs, water quality improvement,
increased recreational opportunities and enhanced
wildlife and biodiversity conservation. With this
outlook we also have the additional opportunity to
think in the long-term and to consider the urban
forest as part of the larger landscape.
Figure 1.
Traditionally the urban forest has been viewedas trees in the city - often along streets and in small groups
in other public places such as parks.
A first step in reorienting our view of urban
forests and their management is to review some
important ecological principles and to see how they
apply to restoration and management. The goal of
this chapter is to examine urban forests as ecosystems
and to discuss some of the opportunities for
managing urban forest ecosystems to provide more
natural benefits to communities and cities.
Figure 2.
Another way to look at the urban forest is as anecosystem with many more components (people, animals,
microorganisms), a physical environment (sidewalks, soil,
rocks), energy flow (sun) and processes (water, nutrient
cycles).
The Urban Forest As An Ecosystem
An urban forest ecosystem (UFE) is a collection
of living matter (plants, animals, people, insects,
microbes) and nonliving matter (soil, rocks and dead
organic matter) through which there is a cycling of
nutrients and water and a flow of energy from the
sun. Based on this definition the UFE represents not
only the trees but also the other components
(including humans, microbes, wildlife and the
physical environment) and the interaction of these
components.
What are the boundaries of a UFE? We can
consider UFEs to be the whole city or smaller parcels
within the city. The boundaries of the UFE depend
Chapter 2: Basic Ecological Principles for Restoration 3
on the nature and scope of our management goals.
No matter what the boundaries of the ecosystem are,
each ecosystem is linked to other surrounding
ecosystems
(Figure 3). As we noted above, urbanand rural ecosystems also overlap and interact to
form landscapes. All the ecosystems on earth
together form the biosphere, which contains all of the
life on earth.
Figure 3.
We can consider the UFE to be the whole city orsmaller parcels within the city depending on our
management goals. The UFE is linked to other
surrounding ecosystems which together form the
landscape.
Why View the Urban Forest
Ecosystem as an Ecosystem?
Cities are part of what used to be rural
landscapes, most of them originally forested
(Figure4)
.Figure 4.
Cities are part of what used to be rurallandscapes. Here you can see the natural forest edges of
this small city. Photo by Hans Riekerk
By comparing the present state of the urban
ecosystem to natural ecosystems, we can learn how
to manage the UFE for some of the natural benefits it
can provide
(Figure 5). These include energyconservation, stormwater management, wildlife
conservation, and recycling or solid waste
management. Also, by taking an ecosystem view, we
can better understand the importance of the structure
and function of UFEs which may help solve local
problems such as flooding, and air and water
pollution. By focusing on urban ecosystem
management we can also contribute to solving larger
scale problems such as biodiversity conservation and
reduction of atmospheric CO
2 concentrations.Figure 5.
By comparing the present state of the urbanecosystem to natural ecosystems, we can learn how to
manage the UFE for some of the natural benefits it can
provide. Photo by Larry Korhnak
The Structure and Function of the
UFE
The UFE is an open system (in thermodynamic
terms) with materials and energy constantly entering
and leaving
(Figure 6).Energy from the sun is fixed by plant leaves in
the UFE. Some of the absorbed energy then flows
out of the ecosystem as heat, which warms the air
(Figure 7)
.The rest of the absorbed solar energy is used to
evaporate or transpire water. Materials entering the
UFE may be in the form of nutrients (fertilizers),
water (in rainfall or irrigation), plants (new plantings
or seeds from invasive plants) or other forms of
non-solar energy, such as fossil fuels
(Figure 8).Chapter 2: Basic Ecological Principles for Restoration 4
Figure 6.
The urban forest ecosystem is an open systemwith energy and materials constantly entering and leaving
the system.
Figure 7.
Energy from the sun is fixed by plant leaves inthe UFE.
Figure 8.
Fossil fuels are one of the materials entering theUFE for management.
Forms of these same materials may leave the
UFE in runoff (storm water), with the wind (seeds)
or in trucks going to landfills (yard and solid waste)
with much converted to CO
2 and heat (Figure 9).Figure 9.
Pruned branches and leaves are materials oftenleaving the UFE to end up in landfills.
The UFE may have a very complex structure
with a variety of layers including a tree canopy, a
shrub understory, an herb layer and a litter layer. The
UFE is made up of living things, called biotic
components (living plants and animals) and
nonliving things, called abiotic components (soil, air,
nutrients, water, dead organic matter). Nutrients
(such as nitrogen, phosphorus and calcium) and
water cycle from the abiotic parts of the ecosystem
to the biotic parts and back again. These are called
nutrient and water cycling, respectively.
There are two major groups of the living things
in the UFE: (1) producers (also called autotrophs)
and (2) consumers (also called heterotrophs)
(Figures 10
and 11).Producers, which are mainly green plants, take
light energy and store it through the process of
photosynthesis. Consumers cannot photosynthesize
but instead feed directly on the producers (i.e.,
herbivores) and other consumers (i.e., carnivores or
detritivores or decomposers). Consumers include
non-photosynthetic bacteria, fungi, and animals,
Chapter 2: Basic Ecological Principles for Restoration 5
Figure 10.
One of the two major groups of living things inthe UFE is producers (also called autotrophs).
Figure 11.
The other major group of living things in theUFE is consumers (also called heterotrophs) which cannot
photosynthesize but instead feed directly on the producers
(i.e., herbivores) and other consumers (i.e., carnivores and
decomposers).
including humans. Producers and consumers are
linked together in complex networks called food
webs
(Figure 12). Food webs are important torecognize in UFE management, because the
disruption or elimination of one part of the web may
impact other organisms and ecosystem functioning in
unexpected ways.
Figure 12.
Producers (mainly green plants) andconsumers (organisms dependent on living and dead plant
and animal matter) are linked together in complex
networks called food webs.
Comparing Natural and Urban Ecosystems
Natural ecosystems have a balance of
production and consumption constantly operating. If
by chance the ecosystem produces more than it
consumes, the excess energy is stored as carbon (in
the wood of tree stems, peat in bogs, etc.). If a fire
or another disturbance lowers plant production, the
consumer populations will adapt accordingly. Cities,
on the other hand, are largely consumers relying on
production of food, energy and natural resources in
outer agricultural, forested and other natural areas
(Odum 1983)
(Figure 13). Seldom do cities producethese necessities within their perimeter in quantities
sufficient to support large numbers of people. At the
same time, cities must contend with the wastes that
are produced, often sending solid wastes and waste
water out of the city.
Figure 13.
Cities rely on natural and domesticatedenvironments for resources. At the same time these cities
must contend with the wastes that are produced, often
sending solid wastes and waste water out of the city
(adapted from Odum 1983).
Chapter 2: Basic Ecological Principles for Restoration 6
How Can the UFE Help?
The urban forest ecosystem can provide many
opportunities for ameliorating the drain and stress on
our natural resources. For example, by cooling the
city with a forest canopy, we are less dependent on
outside natural resources for air conditioning
(Figure14)
.Figure 14.
By cooling the city with a forest canopy, we areless dependent on outside natural resources for air
conditioning. Photo by Hans Riekerk
By providing natural areas for water infiltration,
storage and evaporation of rainwater, the waste water
from our streets and other impervious surfaces is
reduced
(Figure 15).Figure 15.
By providing natural areas for water infiltration,storage and evaporation of rainwater, the waste water
from our streets and other impervious surfaces is reduced.
Photo by Larry Korhnak
By providing places for recreation, fewer people
will need to use fossil fuels to leave the city for their
nature experiences
(Figure 16).Figure 16.
By providing places for recreation, fewerpeople will need to use fossil fuels to leave the city for
their nature experiences. Photo by Larry Korhnak
By supporting, for example, water quality,
forest management, and growth management policies
for lands outside our cities, we will sustain our
natural and domesticated ecosystems. Infusing our
cities and communities with more urban forest
ecosystems will restore natural structure and
processes to our urban forests making us less
dependent on our limited natural resources outside
the city.
Characteristics of the UFE
The Urban Heat Island
Cities can reach temperatures 7
o to 15o F higherthan in the surrounding rural ecosystems. This is
called the urban heat island effect
(Figure 17).Figure 17.
A city is 7o to 15o F warmer than thesurrounding countryside. Adapted from Oke 1982.
Chapter 2: Basic Ecological Principles for Restoration 7
Some of the reasons for this heat buildup are:
(1) cities generate heat from burning fossil fuels
(factories, cars, heating and air conditioning),
(2) city structures absorb and store solar heat
(especially dark surfaces such as asphalt roads and
dark roofs),
(3) through decreased vegetation and rapid
routing of rainwater to storm sewers, cities have
much less natural cooling due to the evaporation and
transpiration of water,
(4) air pollutants may slow the outflow of heat
away from urban surfaces, and
(5) cities usually have less air movement to take
heat out of the city (Lowry 1967; Oke 1982).
Large numbers of trees can reduce local air
temperatures by 1
o to 9o F (McPherson 1994).Evapotranspiration by trees lowers air temperatures
in two ways. First, when precipitation is intercepted
by trees and other plants, the evaporation of this
water cools the air. Secondly, trees constantly take
up water from the soil and lose water to the air. This
process, called transpiration, also lowers air
temperature. Therefore, the UFE can reduce heat
buildup in the city by storing less heat, using more of
the sun's energy for evaporative cooling, and shading
buildings and other surfaces so that they require less
fossil fuel energy for cooling
(Figures 18 and 19).Figure 18.
The urban forest ecosystem throughevaporative cooling and shade can contribute to reducing
the temperatures in the urban heat island. This parking lot
is a contributor to high temperatures in the urban heat
island.
Figure 19.
The urban forest ecosystem throughevaporative cooling and shade can contribute to reducing
the temperatures in the urban heat island. This parking lot
demonstrates trees properly placed to reduce temperature.
Nutrient Cycling in the UFE
Chemicals circulate from the plants and animals
to the soil and back again, as part of the nutrient
cycle
(Figure 20). The health of plants in theecosystem is mainly dependent on the soil for its
source of nutrients. Dead organic matter in the soil,
also called detritus, is the long-term storage site for
essential nutrients. Decomposers (primarily
microrganisms) break down the detritus and release
the nutrients held in the organic matter into organic
forms that can be reused by plants, thus completing
the nutrient cycle. In the UFE, this cycle is often
disrupted or arrested because most of the dead
organic material such as lawn clippings, leaves,
branches, and logs are removed and hauled to landfill
sites or chipped for application to other sites. By
doing so, we are denying the UFE of a readily
recyclable source of fertilizers, which then must be
imported in the form of man-made fertilizers.
What happens when we remove these natural
materials from a backyard, a park, or a schoolyard in
the UFE?
• the soil may be exposed, resulting in erosion,
• plant roots may be exposed and desiccated or
damaged
(Figure 21),• fossil fuels are used to blow leaves, clean the
site and transport the yard waste to landfills or
compost piles
(Figure 22),Chapter 2: Basic Ecological Principles for Restoration 8
Figure 20.
Chemical elements in ecosystems circulatefrom the plants and animals to the soil and back again, as
part of the nutrient cycle.
• the organic matter removed no longer helps the
moisture and nutrient holding capacity of the
soil,
• wildlife and other organisms that depend on
decaying wood or litter for habitat and/or food
cannot live in this neatly maintained
environment,
• precious plant nutrients are removed often
requiring fertilizer applications for replacement
(Figure 23)
,• fertilizers, water, mulches, and pesticides
brought in to support and maintain this altered
system are manufactured at a great fossil fuel
cost.
Figure 21.
When natural plant materials are removed froma landscape, many plant roots may be exposed and
desiccated or damaged.
Figure 22.
Many leaves and branches that could be piledor spread (recycled) in a homeowner's landscape are
instead transported to landfills or urban compost piles.
Figure 23.
Precious plant nutrients are removed from thelandscape either resulting in plant deficiencies or requiring
fertilizer applications.
Instead of using tremendous amounts of energy
to remove branches, leaves, and snags, we can utilize
these materials to sustain the health of the UFE.
These natural mulches can be recycled on-site for
free where they will serve as natural fertilizers.
When they remain on-site, these natural materials
provide all the benefits that we ascribe to mulches in
gardens and landscapes
(Figure 24).It is quite feasible to take advantage of natural
nutrient cycling processes in UFE, contributing in the
process to conservation (water, energy, and soil) and
improving the environment both locally and globally.
Landscapers need to change many ingrained
practices, such as leaving more dead plant materials
on the ground. Creating "natural" or "semi-natural"
Chapter 2: Basic Ecological Principles for Restoration 9
Figure 24.
When leaves, branches, and grass-clippingsare left on-site, these natural materials provide all the
benefits that we ascribe to mulches in gardens and
landscapes.
areas in parks, backyards and other appropriate sites
will have favorable results for nutrient cycling and
other UFE processes such as cycling.
Water Cycling in the Urban Forest
Water forms a critical link between the earth's
surface and the atmosphere. After water falls to earth
as rain (and in other forms), it flows downhill into
creeks or soaks into ground, entering the ground
water (
Figure 25).Figure 25.
In the water cycle, water falls to the earth asprecipitation, enters the ground or flows as runoff to rivers,
lakes and the ocean, and is taken up (used) by plants and
other organisms. By evaporation from vegetation, land
and bodies of water, water re-enters the atmosphere to
begin the cycle once again.
Water in creeks flows into rivers, lakes and
finally the ocean. Water reenters the atmosphere by
evaporation from the land and sea and and by
evaporation and transpiration from vegetation (see
Chapter 6 - The Hydrological Cycle
). In the UFE,impervious surfaces such as buildings, paved streets
and parking lots interrupt this water cycle by
collecting the water and channeling it into sewers,
canals and other structures.
The consequences of interrupting the natural
water cycle include:
1. decreased infiltration of water into soil,
2. more runoff, which must then be managed and
accomodated,
3. decreased water quality as pesticides, fertilizers
and other polluants are concentrated in the
collected runoff,
4. erosion of unprotected soils and
5. less evaporation of water with its associated
cooling effect.
How does the UFE help restore the water cycle?
First, vegetation in the UFE intercepts rainfall and
evaporation of this water helps cool the city. Second,
soils absorb water; then it is either taken up by plants
or percolates to the water table or creeks instead of
running into storm sewers. The result is lower
stormwater treatment costs and less flooding
potential in the city (
Figures 26 and 27).Figure 26.
In the city, impervious surfaces such asbuildings, paved streets and parking lots interrupt the
water cycle by collecting the water and channeling it into
sewers, canals and other structures. Photo by Larry
Korhnak
Chapter 2: Basic Ecological Principles for Restoration 10
Also, if soils are protected with mulches and
plants, less erosion will result in less sediment
entering the water. Wetlands also serve as storage
areas for water. Restoring and managing wetlands in
cities will lower the rate and volume of stormwater
runoff, control floods and erosion and help purify
water that will reach the water table. For example,
after storm in Dayton, Ohio the existing urban forest
reduced runoff by 7%. A slight increase in the urban
forest canopy could reduce runoff by 12% (Sanders
1984).
Figure 27.
Soils in the UFE absorb water; then it is eithertaken up by plants or percolates to the water table or
creeks instead of running into storm sewers. Photo by
Larry Korhnak
Educating policy makers, city managers and the
public about the benefits of vegetation in the UFE
and cost-saving potential is essential to more efective
management of the water cycle. For further
discussion on the water cycle, see
Chapter 6- TheHydrological Cycle
.Carbon Storage and Sequestering by UFEs
Carbon dioxide (CO
2) in the atmosphere isincreasing globally and is the principal contributor to
the expected increase in the greenhouse effect
(global warming). The two main sources of CO
2 arethe burning of fossil fuels and deforestation
(Houghton et al. 1996). Trees, litter, soil and organic
matter all store carbon (C). Since organic matter
contains 50% C, the more biomass (plant and animal
matter) on the earth, the less CO
2 in the atmosphere.In an ecosystem, carbon is taken in as CO
2 inthe process of photosynthesis
(Figure 28). Carbon iseither stored as living or dead plant material or
consumed by other organisms in the food web. CO
2is also given off during respiration. Forests can store
much greater amounts of C in the vegetation and
soils than any other type of ecosystem on earth due
mainly to the relatively massive storage in tree stems.
Figure 28.
In an ecosystem carbon is taken in as CO2
in
the process of photosynthesis. Carbon is either stored as
living or dead plant material or consumed by other
organisms in the food web. CO
2
is also given off during
respiration.
Can the UFE help to store more carbon? Forests
store carbon in their plants, roots, forest litter and
animals. One urban study estimated that the 69
million acres of urban forest in the U.S., with an
average of 28% canopy cover, store annually a net
6.5 million tons of C (Rowntree and Nowak 1991).
However, the whole world puts out 5.4 billion tons C
per year (deforestation alone accounts for 1.6 billion
tons) (Sundquist 1993). Urban forests in the USA
therefore currently only remove 0.1% of the output.
Even though urban forests are not likely to be better
managed just for C sequestration, it is important to
recognize that C sequestration by the UFE is an
additional benefit, albeit small.
To summarize, the UFE can contribute to reduce
atmospheric CO
2 in two ways: First, by reducingfossil fuel (energy) use in the cities
(Figure 29);Second, by increasing C storage from planting and
managing trees especially in cities where tree cover
is currently low.
Chapter 2: Basic Ecological Principles for Restoration 11
Figure 29.
The UFE can contribute to reduce atmosphericCO
2
by reducing fossil fuel (energy) use in the cities.
Wildlife in the UFE
Urbanization and urban sprawl have resulted in
habitat loss, highly fragmented forests, drained
wetlands and disrupted migration routes for wildlife.
Also, in many situations wildlife is dependent upon
two or more ecosystems, and these may not be
available. A forest fragment is a small parcel
separated from the larger forest (see also
Chapter 3- Biodiversity
). In the UFE, forest fragments oftenbecome small parks or undeveloped and often
degraded land. These fragments may be too small or
too distant to support many wildlife species
characteristic of natural areas. However, by
connecting some smaller fragments, larger
ecosystems can be simulated and some migration
routes and habitats restored
(Figures 30 and 31). Forfurther discussion on wildlife, see
Chapter 8 -Wildlife
.Figure 30.
This creek outside of a small city is connectedto a wetland inside the city allowing migration of some
wildlife species. Photo by Hans Riekerk
Figure 31.
By connecting some smaller fragments, largerecosystems can be simulated and some migration routes
and habitats for wildlife may be restored. Photo by Larry
Korhnak
Biodiversity
Until recently, efforts in biological conservation
have largely focused on preservation and protection
of individual species, subspecies and populations,
through the implementation of the Endangered
Species Act. However, scientists and practitioners
are realizing today that this has not always been
successful or even possible, and that many other
species have been ignored as a result. More recently
there is a greater focus on ecosystem management
with the idea that by managing and restoring whole
ecosystems, biodiversity and whole food webs, as
well as individual species, may be better protected.
Urban forests, which range from highly degraded
woodlots to monocultures of exotic trees to
semi-natural ecosystems, may play an important role
in managing for biodiversity. Although urban forests
cannot be expected to support all species groups (for
example large mammals or other wide-ranging
animals), if effectively managed, they can provide
habitat at a smaller scale, increase the effectiveness
of larger nearby reserves, and help with the
movement and conservation of some organisms
through enhanced connectivity
(Figure 32).Thus urban forests can be "stepping stones
between ecosystems" (Franklin 1993)
(Figure 33).At a smaller scale, biodiversity can also be restored
by enhancing the ecosystem's natural structure,
creating multi-age ecosystems in several stages of
succession, controlling invasive plant and animal
species, leaving stumps, leaves, snags and logs to
Chapter 2: Basic Ecological Principles for Restoration 12
Figure 32.
Although urban forests cannot be expected tosupport all species groups (for example large mammals or
other wide-ranging animals), if effectively managed, they
can provide habitat at a smaller scale, increase the
effectiveness of larger nearby reserves, and help with the
movement and conservation of some organisms through
enhanced connectivity. A corridor of forest provides this
connectivity. Photo by Henry Gholz.
improve nutrient cycling and for wildlife and by
planting native species that mimic composition of
nearby ecosystems. (For further discussion, see
Chapters 3 - Biodiversity
, 4 - Plant Succession andDisturbances
, and 9 - Invasive Plants.)Figure 33.
Urban forests can be "stepping stonesbetween ecosystems" (Franklin 1993).
Opportunities for Restoring and
Managing the UFE More
Ecologically
How can we restore and manage the urban forest
ecosystem? We propose the following seven
guidelines:
Restore and manage the UFE to decrease
consumption and contribute to conservation:
• Take advantage of natural nutrient cycling
by leaving grass clippings, leaves, branches
and logs on the ground and thereby reduce
the tremendous amount of energy expended
to remove plant materials from the
landscape.
• Plant and maintain trees around buildings
to reduce energy consumption for cooling
and heating.
• Save energy used for stormwater
management by increasing areas within the
UFE for water infiltration and evaporation.
• Manage the UFE to encourage recreation
in the city, thereby decreasing energy
consumption for travel to distant recreation
sites.
• Plant tree species that are adapted to local
conditions and require only natural rainfall
(after establishment) to save water and