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Fire
Sale! The Admissibility Of Evidence Of Environmental Contamination To Determine Just Compensation In Washington Eminent Domain Proceedings
By Paul W. Moomaw for Washington Law Review - October, 2001
Copyright ©2001 Washington
Law Review Association; Paul W. Moomaw
Abstract: Jurisdictions across the United States
are split on the issue of whether evidence of environmental contamination
should be admissible to determine just compensation in an eminent domain
proceeding. Jurisdictions that admit this evidence reason that environmental
contamination is a property characteristic that necessarily affects the value
of the property. Those that exclude the evidence cite procedural due process
concerns and the risk of extra liability for
the landowner. Washington's
Model Toxics Control Act (MTCA) establishes a system of assigning liability and
recovering cleanup costs for environmental contamination. No Washington court has addressed whether
evidence of environmental contamination should be admissible to determine just
compensation in an eminent domain proceeding. This Comment argues that, under
MTCA and Washington eminent domain law, the evidence should not be admitted,
because its admission (1) would violate the prohibition in Washington eminent
domain law against speculative evidence, (2) would infringe upon the procedural
due process rights of landowners under MTCA, and (3) may result in additional
liability on the part of the landowners and extra recovery on the part of the
condemning authority.
The Smith family owns a small, independent
service station alongside a Washington
highway, selling gasoline and services to motorists who pass by. [FN1] Recently,
motorists using the highway have increased in number, and the Smiths are
delighted to see business booming. However, the increase in traffic has also
put pressure on the highway system, and it is clear that the two-lane, winding
country road is no longer sufficient. State officials have determined that the
only solution is to widen the highway to four lanes. Unfortunately, the Smiths'
service station is in the path of the planned highway expansion. The Smith
family soon receives notice that their property is needed for the highway
project, but that they will receive fair market value for the land.
Unbeknownst to the Smiths, the land beneath
the service station has become a small environmental catastrophe. As appraisers
for the State investigate the land to determine its fair market value, they
discover that the underground fuel storage tanks are leaking and have been
doing so for years. Accordingly, the appraisers come up with a market value for
the land that is significantly less than it would be without the newly
discovered contamination. Meanwhile, officials from Washington's *1222
Department of Ecology (DOE) have begun an investigation of their own, with the
ultimate intention of holding the Smiths liable for the costs of cleanup under
Washington's environmental cleanup statute.
Two legal forces have collided on this Washington highway at
the intersection between modern environmental regulations and traditional
eminent domain law, leaving the Smiths and their family business as the
unwitting victims. Under traditional eminent domain principles, an entity that
takes land through the exercise of eminent domain must pay a landowner
"just compensation," [FN2] which is generally deemed to be the fair market value of
the land, based upon all of the "elements reasonably affecting
value." [FN3] Certainly, environmental contamination is a characteristic
that affects the market value of land. On the other hand, Washington's environmental cleanup statute,
the Model Toxics Control Act (MTCA), [FN4] makes liability strict, joint, and several, [FN5] and holds past and current landowners alike liable for
cleanup. [FN6] Hence, the Smiths find themselves in the position of
receiving less value for their land, while concurrently being held responsible
for the cleanup of the contamination.
Jurisdictions across the United States
are split on the issue of whether evidence of environmental contamination
should be admissible to determine just compensation in an eminent domain
action. Some courts have determined that environmental contamination is a
property characteristic that bears upon the land's market value. [FN7] Therefore, those
courts deem evidence of contamination admissible. [FN8] Courts in other jurisdictions have concluded that
adjudicating the issue of environmental contamination in an eminent domain
proceeding raises various troubling issues, including procedural due process
concerns and the risk of double liability for the landowner. [FN9] Therefore, these courts hold that the evidence should be
excluded. [FN10] Thus far, no Washington
court decision has addressed this issue.
*1223 This Comment argues that, under Washington law, evidence
of environmental contamination should not be admissible to determine just
compensation in an eminent domain proceeding. Part I provides an overview of
eminent domain law in Washington, covering its statutory basis, procedural
aspects, and judicial interpretation, with particular attention to what
constitutes just compensation. Part II discusses MTCA, and gives a synopsis of the relevant regulatory procedures the DOE has
enacted. Part III outlines the current state of jurisprudence on the issue of
admitting evidence of environmental contamination in eminent domain proceedings
in jurisdictions across the United
States. Finally, Part IV argues that, given
the current state of the law in Washington, evidence of environmental
contamination is inappropriate in an eminent domain proceeding because (1) it
would violate the prohibition in Washington eminent domain law against
speculative evidence, (2) it would infringe upon the procedural due process
rights of landowners under MTCA, and (3) it may result in extra liability on
the part of the landowner and extra recovery on the part of the condemning
authority.
I. EMINENT DOMAIN LAW IN WASHINGTON STATE
Eminent domain is the inherent power of a
government to take private property for public use. [FN11] The power of
governmental entities to take property through the exercise of eminent domain
is limited by the federal and state constitutions. [FN12] Every eminent domain proceeding includes a determination
that the property will be used for public purposes, and an assessment of just
compensation to the owner. [FN13] Just
compensation is defined as the fair market value of the property, or what a
willing buyer would pay a willing seller for the property in an open-market
transaction. [FN14] Washington
courts rely on numerous valuation methodologies to determine fair market value. [FN15]
*1224 A. Sources of Authority for Eminent
Domain
The State of Washington inherently possesses the
authority to take private land through the exercise of eminent domain as an
attribute of state sovereignty. [FN16] However, under the United
States and Washington
constitutions, property taken pursuant to eminent domain must be necessary for
"public use," and the governmental entity must pay the landowner
"just compensation." [FN17] The state
government may delegate the power to local government entities, which do not
possess the inherent power of eminent domain. [FN18]
The Washington Legislature has enacted
legislation governing the state's own eminent domain power and delegating the
power to various other entities. [FN19] The legislation requires governmental entities to perform
certain procedures before condemning property under eminent domain. For
example, the condemnor must provide the landowner with adequate notice. [FN20] Moreover, the legislation requires a hearing to determine
whether the property is necessary for "public use" and an opportunity
for a jury trial to assess "just compensation." [FN21]
*1225 B. The Exercise of Eminent Domain
A Washington eminent
domain proceeding consists of three discrete phases: a finding that the
property to be condemned is necessary for public use, an assessment of just
compensation, and an order to transfer title. [FN22] The condemning authority initiates an eminent domain
action by submitting a petition for appropriation to the superior court of the
county in which the property sits [FN23] and serving
notice upon all interested parties. [FN24] Next, a hearing
is held to ensure that the condemning authority has notified all parties with
an interest in the subject property and that the property is truly necessary
for public use. [FN25] If the
government successfully shows that the land is necessary for public use, the
court will issue an order adjudicating that the contemplated use of the
property is truly a public use, [FN26] as well as an
order to determine damages for the taking of the property. [FN27]
If the court issues an order for the
determination of damages, a jury trial is held to determine the proper amount
of just compensation for the property. [FN28] This portion of the proceeding tends to be the most hotly
debated: the great majority of eminent domain cases focus upon the issue of the
proper measure of just compensation. [FN29] Both the
landowner and *1226 the condemning authority may present evidence
bearing upon just compensation, as neither party has the burden of proof with
respect to valuation. [FN30]
C. Just Compensation
An entity that condemns private property
under eminent domain must pay the landowner "just compensation." [FN31] Just
compensation is based upon the fair market value of the property, as defined by
the amount a willing buyer would pay a willing seller on the open market. [FN32] The driving principle behind the constitutional just
compensation requirement is that the property owner is entitled to be placed in
the same monetary position as he or she would have been had the property not
been taken. [FN33] Consequently, the condemnee must receive full value for
the property. [FN34]
1. Valuation
Washington
courts accept numerous valuation methodologies for purposes of measuring the
fair market value of property. The most common valuation methods used in Washington are the
capitalized rental value method, the depreciated replacement cost method, and
the comparable sales method. [FN35] Under the capitalized rental value approach, the value of
the land is measured according to the income it produces. [FN36] Under the depreciated replacement cost method, an
appraiser determines the replacement cost of improvements, adjusts for
depreciation, then adds the market value of the land itself. [FN37] Finally, under the comparable sales method, a land's value
is determined by comparing it to properties *1227
that have been sold within a reasonable period of time, and that are similar in
location, use, improvements, and other qualities. [FN38]
Parties may present testimony regarding the
value of the property through expert witnesses, the property owner, or
neighboring property owners. Although experts typically testify about the value
of property, [FN39]
"[a]n owner of property may testify as to its value (without qualifying as
an expert), upon the assumption that he is particularly familiar with it and,
because of his ownership, knows of the uses for which it is particularly
adaptable." [FN40] Neighbors may
also be particularly knowledgeable with respect to the value of the property,
and may be allowed to testify thereto. [FN41] For example, the
Washington Supreme Court has upheld admission of testimony of a neighbor who
had only seen the subject property from the road, reasoning that the decision
to admit the testimony was within the trial judge's sound discretion, and that
such testimony would go to the weight rather than the admissibility of the
evidence. [FN42]
2. Speculative Evidence
While Washington
courts allow the trier of fact to consider a wide array of factors that may
affect the fair market value of property, [FN43] these factors must meet two basic requirements: (1) they
must actually affect the property's fair
market value, and (2) they must be established by the evidence. [FN44] Hence, evidence that is overly speculative is not admissible
to determine fair market value. [FN45] For example, in
In re City of Medina, [FN46] the court held
that the fair market value of unimproved property could not be determined by
comparing it with town lots that were fully platted and developed. [FN47] Basing a determination of the property's fair market *1228
value on such evidence, the court held, would involve "pure
conjecture." [FN48]
In State v. Mottman Mercantile Co., [FN49] the Washington
Supreme Court stated that land containing mineral content may not be valued by
multiplying the number of cubic yards of the mineral in the land by a unit
price of the mineral as extracted. [FN50] Mottman involved
a piece of property to be condemned that had potential value as a gravel pit.
The court stated that evidence of the present value of the mineral content in
its natural state was admissible on a cubic yard basis. [FN51] However, evidence of the gravel's market value as
extracted would be inadmissible for determining the land's fair market value,
because such evidence would require speculation about the cost of extraction,
the extent and duration of market demand for the minerals, marketing costs, and
other variable factors. [FN52]
Other decisions indicate that Washington courts
consider the fear of potentially dangerous conditions upon land to be overly
speculative and, therefore, inadmissible to
determine just compensation in an eminent domain proceeding. [FN53] In Pacific
Northwest Pipeline Corp. v. Myers, [FN54] a corporation
condemned an easement for the installation of a gas pipeline. The court
approved a jury instruction directing the jury to ignore a witness's testimony
regarding the effect that fear of gas transmission lines had on the market
value of the subject property. [FN55] Additionally, in
State v. Evans, [FN56] the Washington
Supreme Court reversed a lower court's decision that had admitted evidence of
fear. [FN57] The lower court had declared that "[t]he
psychological effect of an adverse condition, real or *1229 imagined, on
a potential buyer may [materially influence] the market value of
property." [FN58] Although the
Washington Supreme Court did not directly address the lower court's assertion
that "real or imagined" psychological effects may be considered in
assessing fair market value, it expressed concern that the jury was permitted
to consider speculative elements. [FN59] The court
reaffirmed Washington's
standard that the only elements that a jury should consider "are those
which will actually affect the fair market value of the property and which are
established by the evidence." [FN60]
II. THE MODEL TOXICS CONTROL ACT
The Model Toxics Control Act (MTCA) [FN61] is Washington's counterpart to the federal environmental
cleanup statute, the Comprehensive Environmental Response, Compensation, and
Liability Act (CERCLA). [FN62] MTCA provides a
statutory framework to allocate liability for environmental contamination, to
raise funds for the cleanup of contamination, and to prevent future
contamination. [FN63] MTCA makes
owners of contaminated property and other parties that are responsible for the
contamination liable for its cleanup. [FN64] It also creates
certain limited defenses to liability. [FN65] Furthermore,
MTCA requires the prioritization of particularly contaminated sites [FN66] and compels remedial action upon those sites that are
deemed to warrant investigation and *1230 cleanup. [FN67] MTCA provides due process to landowners by giving them the
right to assert defenses to liability. [FN68]
A.
Liability and Defenses Under MTCA
Under MTCA, any current owner or operator of
a contaminated site, and any past owner who contributed to the contamination,
is a potentially liable party (PLP) for the purpose of remediating the
contamination. [FN69]
Liable parties are subject to strict, joint, and several liability [FN70] for all remedial action costs [FN71] and any damages to natural resources that occur as a
result of the release "or threatened release" of hazardous
substances. [FN72] MTCA requires PLPs to conduct remedial actions or pay the
state to conduct those remedial actions. [FN73] Washington's
Attorney General may recover all remedial action costs from the liable parties
at the request of the Department of Ecology (DOE). [FN74]
MTCA provides certain affirmative defenses
that may absolve the PLP of liability. [FN75] These defenses are primarily limited to those situations
in which the PLP is innocent, oblivious, or both, with respect to environmental
contamination. [FN76] If the PLP can
establish that the contamination was caused by an "act of God," [FN77] an "act of war," [FN78] or "the *1231 act or omission of a third
party," [FN79] the PLP is not liable under MTCA. [FN80] Moreover, if the PLP can show by a preponderance of the
evidence that, upon acquiring the property, the PLP neither knew nor had reason
to know that any hazardous substance had been released or disposed of on the
property, the PLP is not liable under MTCA. [FN81]
MTCA absolves governmental entities from
liability in certain circumstances. The statute states that the term
"owner/operator," for the purposes of MTCA liability, does not
include governmental agencies "which acquired ownership or control
involuntarily." [FN82] It is not clear whether MTCA's involuntary acquisition
exception to a government's MTCA liability includes the exercise of eminent
domain. However, some commentators have indicated that a similar provision in
CERCLA [FN83] may include circumstances in which the government acquires
the property through eminent domain. [FN84] Because Washington courts often look to CERCLA for guidance in
interpreting MTCA, [FN85] it is possible
that such an interpretation would extend to MTCA as well. Thus, it is unclear
whether a governmental entity that acquires contaminated property through
eminent domain is liable for remediation under MTCA.
*1232 B. Assessing Contamination and
Determining Liability Under MTCA
Washington's
legislature has delegated the authority to enforce and administer MTCA to the
DOE, [FN86] which has
promulgated regulations governing the procedural aspects of MTCA. [FN87] The regulations provide for the investigation and
assessment of potentially hazardous sites, and outline the various actions that
may be taken for the remediation of those sites. [FN88] They also establish criteria for determining the proper
cleanup level for a given piece of property. [FN89]
1. Investigation and Assessment
Both MTCA and the DOE regulations outline
methods by which the DOE can identify contaminated sites. The DOE regulations
provide that any owner or operator of a site who discovers the release of a
hazardous substance that poses a potential threat to human health must notify
the DOE within ninety days of the discovery. [FN90] MTCA provides that if the DOE has a reasonable basis to
believe that a hazardous substance has been or may be released, it may enter upon the property to conduct further
investigation, upon notice to the landowner. [FN91] Furthermore, the
DOE regulations provide that the DOE may take any other actions consistent with
MTCA to identify potentially contaminated sites. [FN92]
Upon discovering a potentially hazardous
site, the DOE will investigate the site to decide what action, if any, to take
with respect to the site. [FN93] Within ninety days of discovering the release of a
hazardous substance, the DOE will conduct an initial site investigation
consisting of, at a minimum, a visit to the site to document the conditions
observed at the site. [FN94] Based upon the
results of the investigation, the DOE will *1233 decide to undertake
either (1) a site hazard assessment, [FN95] (2) emergency
remedial action, [FN96] (3) interim
action, [FN97] or (4) no further action. [FN98] The DOE maintains a list of sites requiring remedial
action and sets priorities for remedial action based upon the results of the
site hazard assessment. [FN99] Once the DOE has
credible evidence of liability and is prepared to proceed with remedial action,
it notifies PLPs of their potential liability. [FN100]
The requisite level of cleanup of a piece of
property depends largely upon the nature of the site. [FN101] The proper
level of cleanup is dictated by the specific hazardous substances found at a
site and the specific media, such as soil, air, or water, by which humans and
the environment could become exposed to the
hazardous substances. [FN102] To determine
the proper method to set cleanup levels, the DOE must examine the nature of the
contamination, the current and potential pathways of human and environmental
exposure to the contamination, the current and potential receptors of the
contamination, and the current and potential use of the land. [FN103]
*1234 2.
Remedial Actions
A remedial action is any action intended to
identify and either eliminate or minimize a threat to human health or the
environment caused by the release of hazardous substances. [FN104] Remedial
actions include investigation, monitoring, and cleanup activities. [FN105] The DOE may initiate a remedial action by sending a
negotiation letter or enforcement order to a PLP or by requesting an
"agreed order." [FN106] The
negotiation letter informs the PLP that the DOE wishes to negotiate toward a
consent decree. [FN107] The letter
typically explains the nature of the DOE's conclusions about a contaminated
site, requests a written statement of the PLP's willingness to negotiate, and
asks for the names of other PLPs. [FN108] An enforcement
order requires a PLP to take action on its own. [FN109] Under an agreed order, the PLP agrees to undertake
remediation of the site. [FN110] In return, the
DOE will not take action against the PLP as long as the PLP complies with the
order. [FN111] However, the agreed order is not a settlement and, therefore, will not contain
covenants not to sue or protection from claims of contribution. [FN112] Finally, the DOE may undertake remedial action entirely on
its own if necessary, as in the case of an emergency. [FN113]
A PLP may also initiate a remedial action by
demanding a settlement under a consent decree, by requesting an agreed order,
or simply by taking action itself. [FN114] In a settlement under consent decree, the PLP accepts
responsibility for the contamination and proposes a remedial action plan for
the site. [FN115] In requesting a consent decree, the PLP must also identify
other PLPs and provide information regarding the history *1235 and use
of the site. [FN116] The Attorney
General may accept the settlement if it appears that the proposed plan is in
compliance with cleanup standards under MTCA and would expedite the cleanup
process. [FN117]
Finally, an independent remedial action [FN118] is a remedial
action undertaken by a PLP outside of an order or decree and without the
approval or oversight of the DOE. [FN119] The DOE may,
however, provide a limited amount of informal assistance. [FN120] Within ninety days of completion, a PLP that initiates
such an action must submit to the DOE a report containing a description of its
investigation, remediation, and monitoring conducted on the property. [FN121] The DOE must inform the PLP whether any further action is
necessary within ninety days of receiving the report. [FN122]
C. Recovery of Remedial Action Costs
Under MTCA, the Washington Attorney General
can file an action to recover remedial action costs that the DOE has spent to
clean a contaminated site. The Attorney General is authorized to file an action
if necessary to recover all costs incurred, including the costs of undertaking
any investigative and remedial actions. [FN123] Remedial action costs are any costs "reasonably
attributable" to the site, and include costs of direct remedial
activities, [FN124] support costs,
[FN125] and interest charges. [FN126] The Attorney
General may also bring an action against a PLP that has failed to comply with
an enforcement order or an agreed order issued by the *1236 DOE. [FN127] In such an action, the Attorney General may recover up to
three times the amount that the state must incur to undertake remediation
activities, as well as a civil penalty of up to $25,000 for each day that the
PLP refuses to comply. [FN128]
MTCA provides that any "person" who
undertakes a remedial action on its own may recover cleanup costs and
litigation expenses from PLPs. [FN129] This private right of action encourages private parties to
undertake remedial actions independently. Moreover, the DOE and other
governmental entities may also bring a private right of action, as MTCA's
definition of "person" includes "state government agenc[ies]
[and] unit[s] of local government." [FN130] Hence, any authority that may exercise the power of
eminent domain may also bring a private right of action under MTCA.
A party seeking recovery under the private
right of action may recover only remedial action costs that are substantially
equivalent to those that the DOE would have undertaken. [FN131] To facilitate
private rights of action, the DOE has enumerated a number of elements that a
remedial action should contain in order to meet the substantial equivalent
requirement. [FN132] For example,
information on the site and its remediation must be reported to the DOE, [FN133] the DOE must not object to the action, [FN134] and the public at large must be notified of the
remediation. [FN135]
D.
Procedural Due Process Under MTCA
MTCA provides due process to PLPs by giving
them the right to assert defenses to liability. [FN136] The right to
due process of law is *1237 embedded in the Washington State
and United States Constitutions. The Washington State Constitution provides
that "[n]o person shall be deprived of life, liberty, or property, without
due process of law." [FN137] Similarly, the
Fourteenth Amendment to the United States Constitution states that a state may
not "deprive any person of life, liberty, or property, without due process
of law." [FN138] In Washington, procedural
due process requires that parties whose rights are affected by a governmental
proceeding have a meaningful opportunity to
be heard, and notice calculated to advise the parties of the proceeding to allow
them the opportunity to present defenses. [FN139] If any
"significant property interest" is at stake, the safeguards afforded
by due process are applicable. [FN140]
Encompassed within the constitutional right
to due process is the "guarantee of
fair procedure," or procedural due process. [FN141] Procedural due
process imposes limitations upon governmental action that deprives individuals
of life, liberty, or property. [FN142] In a
procedural due process claim, the question is not whether the deprivation of
"life, liberty, or property" is itself unconstitutional, but whether
the deprivation took place without the procedural guarantees envisioned by the
Constitution. [FN143] The rules of
procedural due process "'minimize substantively unfair or mistaken
deprivations of' life, liberty, or property by enabling persons to contest the
basis upon which a State proposes to deprive them of protected interests."
[FN144]
*1238 In Mathews v. Eldridge, [FN145] the United
States Supreme Court articulated a three-part balancing test for identifying
the requirements of procedural due process. [FN146] Under this
test, a court should attempt to balance (1) the private interests that are
affected by a governmental action, (2) the risk that the procedures employed by
a governmental actor will result in the mistaken deprivation of those
interests, and (3) the government's own interests,
including the economic and administrative burden that the procedural protection
would entail. [FN147] In
implementing this test, the Court has generally held that some minimal
opportunity to be heard is required before the government deprives an
individual of liberty or property. [FN148]
One of the fundamental requirements of
procedural due process is the opportunity to be heard "at a meaningful
time and in a meaningful manner." [FN149] For the opportunity to be meaningful, it must be
appropriate to the nature of the case. [FN150] For example, Bell v. Burson [FN151] involved a due process challenge to a statute that
divested uninsured motorists who were *1239 involved in accidents of
their driver's licenses unless they posted security sufficient to cover the
damage alleged by the other party to the accident. [FN152] The United States Supreme Court held that, under the statute,
motorists were entitled to a hearing wherein they were afforded an opportunity
to present defenses to liability. [FN153] Further,
Goldberg v. Kelly [FN154] involved a
procedural due process claim for the wrongful termination of welfare benefits.
The Supreme Court similarly held that the "meaningful" requirement
dictated that individuals who were being deprived of their public assistance
should have notice of the reasons for the termination and an opportunity to
defend themselves by confronting adverse witnesses and presenting arguments and
evidence. [FN155]
In Washington,
procedural due process requires that parties whose rights are affected by a governmental
proceeding have, at a minimum, a meaningful opportunity to be heard and notice
calculated to advise them of the proceeding, to allow the party to present
defenses. [FN156] Moreover, Washington courts also
hold that the opportunity must be presented "at a meaningful time and in a
meaningful manner." [FN157] If any
"significant property interest" is at stake, the safeguards afforded
by due process are applicable. [FN158] In Olympic Forest Products, Inc. v. Chaussee Corp., [FN159] the Washington Supreme Court articulated the specific
procedures required by due process. It determined that a court must consider
the nature of the affected interest, the manner in which it is affected, the
government's reasons for acting as it did, what procedural alternatives are
available, the amount of protection that ought to be given to the governmental
actor, and the balance between the benefit accomplished and the detriment
suffered. [FN160]
*1240 III.
JURISDICTIONS ARE SPLIT ON THE ADMISSIBILITY OF EVIDENCE OF
ENVIRONMENTAL CONTAMINATION IN EMINENT DOMAIN PROCEEDINGS
There is a split of authority across the United States
on the issue of whether evidence of environmental contamination should be
admissible to determine just compensation in eminent domain proceedings. [FN161] Jurisdictions
that refuse to admit such evidence have expressed concern that it would
circumvent procedures already established by environmental laws and regulations for determining liability for
contamination and result in additional liability for the condemnee.
Jurisdictions that admit the evidence reason that contamination is a property
characteristic--which must necessarily be taken into account to determine fair
market value--and that environmental contamination creates a "stigma"
upon property.
A. Excluding
the Evidence
1. Considerations of Additional Liability
At least one court has refused to admit
evidence of environmental contamination in an eminent domain proceeding in
order to prevent the potential for extra liability for the landowners. [FN162] In Aladdin,
Inc. v. Black Hawk County, [FN163] a county
condemned a contaminated laundry facility in preparation for building a new
jail [FN164] and sought to reduce the compensation it paid for the
property on account of the environmental contamination. [FN165] Because Iowa
law provided for administrative procedures to remedy environmental
contamination, the Iowa Supreme *1241 Court expressed concern that the
landowner would incur additional liability if evidence of the contamination
were admitted. The court reasoned that if the proper administrative procedures
were not followed with respect to the environmental remediation, and the
contamination were figured into the amount
of compensation for the property, "the landowner will not receive just
compensation because the award will be less than full value. In addition, the
property owner will have the same legal liability for cleanup cost as
before." [FN166]
2. Procedural Due Process Concerns
The Aladdin court was also concerned that
admitting contamination evidence would compromise the landowner's due process
rights. [FN167] In Iowa, as in Washington,
the environmental cleanup statute contained procedural safeguards for the
benefit of the landowner. [FN168] The Aladdin
court held that admitting evidence of environmental contamination would deprive
the landowner of just compensation. [FN169] In making its
determination, the Aladdin court cited procedural due process concerns,
expressing the fear that the scope of procedural guarantees available in an
environmental liability adjudication would not be available in the context of
eminent domain. [FN170] The court
reasoned that a landowner has the right to have environmental cleanup liability
adjudicated in a proceeding in which there is an opportunity to show that the
landowner is not responsible for the contamination. [FN171] Therefore, effectively establishing the landowner's
liability in a condemnation proceeding would violate the landowner's procedural
due process rights. [FN172] Furthermore,
if another party is able to prove that the
landowner is legally responsible for the contamination, the remediation costs
can be recovered in an environmental action after completion of the eminent
domain proceeding. [FN173]
*1242 In Department of Transportation
v. Parr, [FN174] the Illinois
Court of Appeals also excluded evidence of environmental contamination in an
eminent domain proceeding due to procedural due process concerns. [FN175] In Parr, the Illinois Department of Transportation
condemned a landowner's contaminated property to construct a bridge. [FN176] The Illinois
environmental statute, like MTCA, set forth a comprehensive process for
remediating environmental contamination and adjudicating liability. [FN177] Among other things, the statute provided for certain
procedural safeguards to protect landowners when adjudicating liability for
environmental contamination. [FN178] The court held
that admitting evidence of environmental contamination would violate the
procedural due process rights of the condemnees, because it would allow the
condemning authority to circumvent the procedural safeguards implemented to
protect the rights of landowners under the statutory scheme. [FN179] The court noted that procedural due process requires that
"orderly proceedings" advance according to rules that do not violate
the fundamental rights of the parties involved. [FN180] Therefore, depriving landowners of the rights and defenses
afforded by the Illinois
environmental statute would constitute a violation of procedural due process. [FN181]
B.
Admitting the Evidence: Environmental Contamination as a Property
Characteristic
Some courts admit evidence of environmental
contamination in eminent domain proceedings on the basis that it is a property
characteristic and necessarily affects the fair market value of property. [FN182]*1243 For example, in State v. Hughes,
[FN183] an Oregon
court of appeals held that the evidence of contamination is admissible in an
eminent domain action. [FN184] In Hughes, the
State of Oregon
condemned contaminated property for a highway improvement project. [FN185] After condemning the property, the condemnor discovered
that petroleum contamination was present in the groundwater beneath the site. [FN186] Citing Oregon's
evidentiary rule for relevance, [FN187] the court
reasoned that, although the contamination was discovered subsequent to the
condemnation, the evidence could have been discovered on the date the action
was commenced and would bear on the fair market value of the property at the
time. [FN188] Therefore, the evidence would "easily pass the
threshold for relevance" and should be admitted in a proceeding to
determine just compensation. [FN189]
In Finkelstein v. Department of
Transportation, [FN190] the
Florida Supreme Court admitted evidence of environmental contamination to
determine just compensation in an eminent
domain proceeding on the basis that there is a "stigma" associated
with contaminated property that affects its market value. [FN191] In Finkelstein, the Florida Department of Transportation
condemned a piece of property in connection with the construction of an
interstate highway. [FN192] The Florida
Supreme Court held that, as long as the facts show that environmental
contamination actually has an effect on the market value of the property to be
condemned, evidence of environmental contamination is admissible to determine
just *1244 compensation. [FN193] The court
supported its conclusion with an earlier decision holding that the public fear
of power lines is relevant to the market value of property. [FN194] The Finkelstein court listed several reasons why the
stigma associated with contaminated property would affect its market value. [FN195] For example, a buyer on the open market would consider the
cost of remediating the contamination and the buyer would be subject to strict,
joint, and several liability for contamination under environmental statutes. [FN196] The contamination would subject the buyer to liability to
the community. [FN197] Finally,
lenders would hesitate to finance the acquisition or improvement of contaminated
property, particularly if the financing arrangement could subject the lender to
liability for the contamination. [FN198]
Recently, in Northeast Connecticut Economic
Alliance, Inc. v. ATC Partnership, [FN199] a municipal government condemned a contaminated parcel of property as part of a regional redevelopment
plan, seeking to pay $1 in compensation due to the contaminated state of the
property. [FN200] *1245 There, the court held that "evidence of
environmental contamination and remediation costs is relevant to the valuation
of real property taken by eminent domain and admissible in a condemnation
proceeding to show the effect, if any, that those factors had on the fair
market value of the property on the date of the taking." [FN201] The court reasoned that failing to admit the evidence
would result in a "fictional" property value, because a purchaser of
property on the open market would base the price it was willing to pay on a
variety of factors, including (1) potential liability for the contamination,
(2) "stigma" related to the property even after it has been
remediated, (3) increased financing costs charged by lending institutions, and
(4) the potential for increased regulation. [FN202]
IV. EVIDENCE OF ENVIRONMENTAL CONTAMINATION SHOULD NOT BE
ADMISSIBLE TO
DETERMINE JUST COMPENSATION IN WASHINGTON EMINENT DOMAIN PROCEEDINGS
Washington
courts should not admit evidence of environmental contamination to determine
just compensation in eminent domain proceedings. First, evidence of
environmental contamination falls short of Washington's rule prohibiting overly
speculative evidence. Second, admitting evidence of environmental contamination
in eminent domain proceedings deprives landowners of defenses and procedural safeguards under MTCA, thereby constituting a
violation of procedural due process. Finally, admitting the evidence may
effectively result in additional liability for the landowner and a windfall to
the condemnor.
A.
Evidence of Environmental Contamination Should Not Be Admitted To Determine
Just Compensation Because It Contradicts Washington's
Prohibition Against Speculative Evidence in Eminent Domain Proceedings
Admitting evidence of environmental
contamination for the purpose of valuing property in an eminent domain
proceeding would require the *1246 jury to engage in impermissible
speculation. [FN203] In
determining just compensation in Washington
eminent domain proceedings, the jury may not consider evidence that "is
remote, imaginary, or speculative." [FN204] Juries may
only consider those elements that have an actual effect on the property's fair
market value and are established by evidence. [FN205] For example, the market value of a parcel of land with
mineral content may not be determined by using an estimated market price for
the mineral as extracted. [FN206] This would
entail speculation about, among other things, the costs of extracting and
marketing the mineral and the nature and extent of demand for the mineral. [FN207]
Similarly, devaluing property based on
contamination would require the jury to speculate about the extent of
contamination, the necessary responses, and
the response costs. Under MTCA, liability for cleanup is based upon all costs
which are "reasonably attributable" to remediation of the property. [FN208] By definition,
costs may not be attributed to remediation of the contamination until cleanup
is complete, as the DOE expects to receive payment of remediation costs as they
are incurred. [FN209] In addition,
cleanup may take years to complete and, consequently, may not be completed
while an eminent domain proceeding is taking place. The full extent of
contamination and necessary expenses may not be known until the cleanup is
complete. [FN210] Therefore, attempting to estimate the costs of cleanup
before remediation is complete and the full extent of the contamination is
known would involve a great deal of conjecture. Moreover, even if accurate
evidence regarding the extent of the contamination is admitted, the jury would
need to speculate to determine the effect of the contamination on the
property's value. As at least one commentator has noted, the potential range of
devaluation due to *1247 contamination can be vast. [FN211] Moreover, the average jury may not be equipped to handle
the complicated technical information involved with environmental contamination
and its effect on market value. [FN212]
Use of the accepted valuation methodologies
in Washington
eminent domain proceedings does not make determining environmental
contamination and its effect on market value in an eminent domain proceeding
any less speculative. For example, under the income capitalization approach,
the value of a plot of land is measured by
projecting the amount of income it is likely to produce, subtracting future
expenses, and capitalizing at an appropriate discount rate. [FN213] Environmental
contamination may theoretically be considered a future expense which is
deducted from the projected income stream. [FN214] However, even
under this formula, the jury would be required to speculate with respect to the
extent of environmental contamination, the necessary remediation measures, and
the costs of cleanup.
The comparable sales approach is of little
help. Under that approach, the value of a given piece of property is determined
by comparing it with similar properties that have been sold within a reasonable
period of time. [FN215] In
the case of contaminated property, it would be necessary to find another piece
of property that is similarly contaminated and similar in other respects, such
as size, location, and zoning. Since the character and extent of contamination
tends to be unique to a given piece of property, it would be exceedingly
difficult to locate similar property upon which to draw a comparison. [FN216] Moreover, comparing contaminated property to
uncontaminated property that is similar in other respects would certainly be
speculative. As one Washington
court has noted, even a comparison of undeveloped land with fully developed
property to *1248 estimate market value leads to impermissible
speculation and conjecture. [FN217] As that court
declared, a court "cannot be too careful in excluding evidence of this character." [FN218]
The depreciated replacement cost method is
similarly unavailing. Under that approach, just compensation is measured by
determining the replacement costs of improvements on the property, subtracting
depreciation, and adding the market value of the underlying property. [FN219] Such an
approach simply begs the question: once the cost of improvements and the amount
of depreciation have been established, the market value of the property itself
must still be determined. Presumably, this will require recourse to the
methodologies previously discussed. [FN220] Thus, the
depreciated replacement cost method falls short, for the same reasons that the
income capitalization and comparable sales approaches fail. [FN221]
Some jurisdictions that admit evidence of
environmental contamination to determine just compensation have much more
liberal standards than Washington
for admitting speculative evidence. [FN222] Therefore, they do not provide persuasive precedent for
admitting such evidence in Washington.
For example, Florida
courts will consider evidence of the public's fear of a condition on land to
determine its market value. [FN223] Based in part
upon that reasoning, the Finkelstein court was willing to admit evidence of
environmental contamination in an eminent domain proceeding, stating that doing
so is consistent with the notion that "any factor including public fear
which impacts on the market value of land taken for a public purpose may be considered . . . ." [FN224] However, Washington
has eschewed the admissibility of speculative *1249 evidence like public
fear. [FN225] Thus, one of the primary rationales relied upon by
jurisdictions admitting evidence of environmental contamination in eminent domain
proceedings is inapplicable in Washington.
B.
Admitting Evidence of Environmental Contamination To Determine Just
Compensation in an Eminent Domain Proceeding Violates the Procedural Due
Process Rights of Landowners
Admitting evidence of environmental
contamination to determine just compensation would circumvent the procedural
safeguards established by MTCA and, therefore, constitute a violation of
procedural due process. To determine whether governmental action constitutes a
violation of procedural due process, a court must first determine whether a
party has been deprived of a property interest. [FN226] Upon finding
such a deprivation, the court must then determine the level of process that is
due. [FN227] Applying the balancing test set forth in Mathews v.
Eldridge, [FN228] admission of evidence of environmental contamination to
determine just compensation will result in the mistaken deprivation of the
landowner's property interests with no significant concomitant governmental
benefit and is therefore a violation of the landowner's right to procedural due
process.
Reducing just compensation in an eminent domain proceeding due to
environmental contamination deprives a landowner of an important property
interest. One of the fundamental principles behind just compensation in eminent
domain is the requirement that the property owner be put in the same monetary
position as she would have occupied had the property not been taken. [FN229] Payment of
anything less than full compensation divests the landowner of that important
interest.
Under the Mathews balancing test, a court
must balance (1) the private interests that are affected by a governmental
action, (2) the risk that the procedures employed by the governmental actor
will result in the mistaken deprivation of those interests, and (3) the
government's own *1250 interests, including the economic and
administrative burden that the procedural protection would entail. [FN230] Reducing just
compensation due to environmental contamination in an eminent domain proceeding
deprives the landowner of full compensation, without affording the landowner
the procedural safeguards outlined in MTCA. MTCA provides a thorough procedural
framework for investigating the existence of contamination and assigning
responsibility for any contamination discovered. It provides the landowner with
numerous options for mitigating the contamination, [FN231] offers certain defenses to liability, [FN232] affords the right to seek contribution from other PLPs, [FN233] and enables the landowner to bring a private right of
action by remediating the property according
to DOE standards. [FN234] An eminent
domain proceeding provides the landowner with none of these procedural
safeguards and, thus, may not be a level of process that is appropriate to the
nature of the interests being divested. [FN235] At the same
time, preventing the governmental entity from paying reduced compensation on
account of contamination does not deprive it of its interests. On the contrary,
whatever interests the government has--for example, remediating contaminated
property and holding landowners responsible for the contamination--is amply
addressed by MTCA. In addition, any financial loss sustained by the condemnor
in paying full value for contaminated property can be amply redressed by
forcing the PLPs to remediate the contamination under MTCA. If the proper
procedures are employed under MTCA, the government wins by recovering cleanup
expenses in an action against the PLP, and the landowner wins by maintaining
her procedural guarantees.
Courts in other jurisdictions have come to
similar conclusions. [FN236] For example, Department of Transportation v. Parr [FN237] involved an environmental statute similar to MTCA in that
it assigned liability for environmental contamination while providing
landowners with certain procedural safeguards. [FN238] There, the court concluded that adjudicating *1251
liability for environmental contamination in an eminent domain proceeding would
constitute a procedural due process violation, because it would circumvent the rights, defenses, and
procedural safeguards established by the statute. [FN239] Because the same holds true under Washington
law, Washington
should adopt the Parr court's reasoning and preclude consideration of
environmental contamination to determine just compensation.
C.
Evidence of Environmental Contamination Should Not Be Admitted in an Eminent
Domain Proceeding Because It May Create Additional Liability for the Landowner
and Result in a Windfall for the Condemnor
Where the landowner is a PLP under MTCA,
admitting evidence of contamination to determine just compensation potentially
subjects the landowner to additional liability. First, the landowner receives a
reduced price for the property in an eminent domain proceeding due to a
determination that the contamination affects its fair market value. Then, the
landowner may be subject to liability in a MTCA action and may consequently be
forced to pay remediation costs for the contamination. The landowner is forced to
sell the land at a price reduced by environmental contamination and
subsequently required to pay for the cleanup of the same contamination.
Therefore, the landowner is effectively subject to additional liability in the
amount that the just compensation is reduced.
Although additional liability may also result
if the landowner simply sells the property on the open market and is later held
liable for remedial action under MTCA, there
are important distinctions between a transaction on the open market and an
eminent domain action. No one is forcing the landowner to sell in a transaction
on the open market. The seller may prefer to remediate the property on her own
and sell at a higher price, rather than selling at a reduced price due to the
contamination and later being held liable under MTCA. Moreover, if no buyer is
willing to pay what the landowner considers a fair price, the landowner may
find it more economically efficient to simply keep the property and take her
chances with future liability.
Furthermore, the landowner can bargain away
future MTCA liability if permitted to sell the land on the open market. For
example, the *1252 landowner may agree to sell the land at a discounted
rate in exchange for the buyer's promise to indemnify the landowner against any
future MTCA liability. [FN240] In this way, the landowner avoids additional MTCA
liability because, although the seller may receive a reduced rate due to the
contamination, he or she can avoid future liability under MTCA. Similarly, the
parties to a voluntary sale may agree to mitigate potential MTCA liability by
taking independent action to remediate environmental contamination. In an
eminent domain action, however, the landowner is deprived of the bargaining
power to negotiate such a trade.
Similarly, admitting evidence of
environmental contamination to determine just compensation may effectively give
the condemning authority a windfall. First,
the condemning authority acquires the property at a reduced price. Then, once
the contamination has been cleaned, the condemnor may subsequently hold the
landowner responsible for remediation costs under MTCA. Not only is the state
Attorney General entitled to recover its remediation costs from the PLP, [FN241] but any
governmental entity that may condemn property by eminent domain may also bring
a private right of action under MTCA. [FN242] In effect, the
condemning authority purchases the property at a price adjusted for
contamination, but ultimately receives a piece of property free of
contamination. Thus, the condemnor receives a windfall in the amount that the
just compensation is reduced for contamination.
V. CONCLUSION
Evidence of environmental contamination
should not be admissible to determine just compensation in a Washington eminent domain proceeding.
Although it is true that environmental contamination may have an impact on the
market value of land, admitting this evidence contravenes Washington's
prohibition against speculative evidence to determine just compensation,
violates the procedural due process rights *1253 of landowners, and may
result in a windfall for the condemnor and additional liability for the
landowner. There is no doubt that the cleanup of contaminated property should
be a public priority of the highest order, for the well-being of Washington and for the
planet as a whole. However, this interest
must be balanced against the interest citizens have in receiving just
compensation when their land is taken by the government. Washington has established a comprehensive
and effective scheme for addressing the problem of environmental contamination,
which provides for the landowners' interests as well as the public interest.
The problem of environmental contamination should be addressed under that
scheme--condemnors should not have the option of circumventing MTCA in order to
obtain property at fire sale prices.
[FN1]. Hypothetical created by the author.
[FN2]. U.S.
Const. amend. V; Wash.
Const. art. I, § 16.
[FN3]. In
re Town of Issaquah, 31 Wash. 2d 556, 564, 197 P.2d 1018, 1022 (1948).
[FN4]. Wash. Rev. Code § 70.105D (2000).
[FN5]. Id.
§ 70.105D.040(2).
[FN6]. Id.
§ 70.105D.040(1); see also infra note 62 and accompanying text.
[FN7]. See infra Part
III.B.
[FN8]. See infra Part III.B.
[FN9]. See infra Part III.A.
[FN10]. See infra Part III.A.
[FN11]. Black's Law Dictionary 541 (7th ed. 1999). The exercise
of the eminent domain power is frequently referred to as
"condemnation." 17 William B. Stoebuck, Real Estate: Property Law, in
Washington
Practice, § 9.1 (1995).
[FN12]. U.S.
Const. amend. V; Wash.
Const. art. I, § 16.
[FN13]. See infra Part I.B.
[FN14]. In
re Town of Issaquah, 31 Wash. 2d 556, 564, 197 P.2d 1018, 1022 (1948).
[FN15]. See infra Part I.C.1.
[FN16]. See City
of Tacoma v. Welcker, 65 Wash. 2d 677, 683, 399 P.2d 330, 334 (1965) ("The power of eminent domain is an attribute of
sovereignty. It is an inherent power of the state, not derived from, but
limited by, the fundamental principles of the constitution."); see also
Stoebuck, supra note 11, § 9.3.
[FN17]. The Washington State Constitution provides that
"[n]o private property shall be taken or damaged for public or private use
without just compensation having first been made." Wash.
Const. art. I, § 16. Similarly, the Fifth
Amendment to the United States Constitution states that "nor shall private
property be taken for public use, without just compensation." U.S.
Const. amend. V. The question of what properly
constitutes "public use" is beyond the scope of this Comment, which
focuses on the "just compensation" requirement.
[FN18]. See Welcker,
65 Wash. 2d at 683, 399 P.2d at 334-35 (stating
that a municipal corporation, unlike the state government, does not have the
inherent power to take property through eminent domain, but "may exercise
such power only when it is expressly so authorized by the state
legislature"); see also Stoebuck, supra note 11, § 9.3.
[FN19]. Wash.
Rev. Code § § 8.04.010-.191 (state),
8.08.010-.150 (counties), 8.12.010-.580
(cities), 8.16.010-.160 (school districts), 8.20.010-.180 (corporations)
(2000). This Comment focuses on the issue from the broad perspective of the
state's power of eminent domain; any difference between it and the more limited
powers of other entities is insignificant for the purposes of this Comment.
[FN20]. Id.
§ 8.04.020.
[FN21]. Id.
§ § 8.04.070-.080. Of course, the parties may forego judicial proceedings if
they settle upon an amount of compensation that is satisfactory to all. Washington's eminent
domain statute provides that "[e]very reasonable effort shall be made to
acquire expeditiously real property by negotiation." Id. § 8.26.180.
[FN22]. Stoebuck, supra note 11, § 9.26.
[FN23]. Wash.
Rev. Code § 8.04.010. The petition must contain
the names of any party that has an interest in the property to be condemned, a
description of the property, a description of the interests to be condemned,
the purposes for which the land is to be
condemned, the authority for the condemnation, a request that a jury determine
the proper amount of just compensation, and a prayer that the court award the
property interest to the condemning authority. Stoebuck, supra note 11, § 9.27.
[FN24]. Wash.
Rev. Code § 8.04.020. Generally, the notice must
contain a statement that the condemnor seeks to condemn the property, a
description of the property to be condemned, and a statement of the place and
time at which the petition is to be submitted to the court. Stoebuck, supra
note 11, § 9.27.
[FN25]. Wash.
Rev. Code § 8.04.070. "[W]hether the
contemplated use be really public shall be a judicial question, and determined
as such, without regard to any legislative assertion that the use is
public." Wash.
Const. art. I, § 16. This language explains the
requirement that there be a hearing to determine whether the land has actually
been taken for a public use. Stoebuck, supra note 11, § 9.20. To meet the
requirement that the property be necessary for public use, the court must make
a determination "(1) that the use is really public, (2) that the public
interests require it, and (3) that the property appropriated is necessary for
the purpose." In
re City of Seattle, 96 Wash. 2d 616, 625, 638 P.2d 549, 555 (1981).
[FN26]. Wash.
Rev. Code § 8.04.070.
[FN27]. Id.
§ 8.04.080.
[FN28]. Id.
[FN29]. Stoebuck, supra note 11, § 9.1.
[FN30]. See State
v. Templeman, 39 Wash. App. 218, 223, 693 P.2d 125, 128 (1984).
[FN31]. Wash.
Const. art. I, § 16.
[FN32]. In
re City of Medina, 69 Wash. 2d 574, 578, 418 P.2d 1020, 1022 (1966) (citing In
re Town of Issaquah, 31 Wash. 2d 556, 564, 197 P.2d 1018, 1022 (1948); 29A
C.J.S. Eminent Domain § 137); see also State
v. Sherrill, 13 Wash. App. 250, 255, 534 P.2d 598, 601 (1975).
[FN33]. State
v. Trask, 98 Wash. App. 690, 697, 990 P.2d 976, 980 (2000)
(concluding that pre- and post-judgment interest are to be included in just
compensation).
[FN34]. Id.
[FN35]. Stoebuck, supra note 11, § 9.30.
[FN36]. See 4 Julius Sackman, Nichols on Eminent Domain §
12.02[1], at 12-72 (3d ed. Rev. 2000).
At its most basic, this method would involve valuing the property according to
how much rental income it could generate, capitalized at a reasonable discount
rate.
[FN37]. See id. Of course, the market value of the underlying
land would have to be determined using one of the other methodologies.
[FN38]. See id..
[FN39]. See, e.g., City
of Renton v. Scott Pac. Terminal, Inc., 9 Wash. App. 364, 370-71, 512 P.2d
1137, 1142 (1973).
[FN40]. State
v. Larson, 54 Wash. 2d 86, 88, 338 P.2d 135, 136 (1959) (citing Weber
v. W. Seattle Land & Improvement Co., 188 Wash. 512, 63 P.2d 418 (1936)).
[FN41]. Pac.
N.W. Pipeline Corp. v. Myers, 50 Wash. 2d 288, 291-92, 311 P.2d 655, 657 (1957).
[FN42]. Id.
[FN43]. See In
re Town of Issaquah, 31 Wash. 2d 556, 564, 197 P.2d 1018, 1022 (1948).
[FN44]. State
v. Williams, 68 Wash. 2d 946, 950, 416 P.2d 350, 353 (1966).
[FN45]. Id.; see also In
re City of Medina, 69 Wash. 2d 574, 578, 418 P.2d 1020, 1022-23 (1966).
[FN46]. 69
Wash. 2d 574, 418 P.2d 1020 (1966).
[FN47]. Id.
at 578, 418 P.2d at 1022-23.
[FN48]. Id.
(quoting Nichols, Eminent Domain § 18.11[2] (3d ed. Rev. 1962)) (internal
quotation marks omitted).
[FN49]. 51
Wash. 2d 722, 321 P.2d 912 (1958).
[FN50]. Id.
at 724-25, 321 P.2d at 914.
[FN51]. Id.
at 725, 321 P.2d at 914.
[FN52]. Id.; see also State
v. Larson, 54 Wash. 2d 86, 88, 338 P.2d 135, 136 (1959).
[FN53]. See, e.g., Pac.
N.W. Pipeline Corp. v. Myers, 50 Wash. 2d 288, 290, 311 P.2d 655, 656 (1957); State
v. Evans, 96 Wash. 2d 119, 127, 634 P.2d 845, 849 (1981), opinion amended, 649
P.2d 633 (1982).
[FN54]. 50
Wash. 2d 288, 311 P.2d 655 (1957).
[FN55]. Id.
at 290, 311 P.2d at 656. Although the court was
unwilling to reverse on the grounds that the testimony was given, its refusal to
do so was predicated on the fact that the limiting instruction had been given. Id.
[FN56]. 96
Wash. 2d 119, 634 P.2d 845 (1981), opinion
amended, 649 P.2d
633 (1982).
[FN57]. Id.
at 128.
[FN58]. State
v. Evans, 26 Wash. App. 251, 261, 612 P.2d 442, 449 (1980)
("These effects and their impact on the market value have been recognized
in cases involving the inherent fear of electricity and gas transmission
lines."), rev'd, 96
Wash. 2d 119, 634 P.2d 845, opinion amended, 649
P.2d 633 (1982).
[FN59]. Evans,
96 Wash. 2d at 127, 634 P.2d at 849.
[FN60]. Id.
[FN61]. Wash. Rev. Code § 70.105D (2000).
[FN62]. 42
U.S.C. § § 9601-75 (1994 & Supp. V 1999).
Although CERCLA may be equally applicable with respect to the issues discussed
here, this Comment focuses primarily on Washington
law. Hence, CERCLA is beyond its scope.
[FN63]. Wash.
Rev. Code § 70.105D.010. A
"contaminant" is "any hazardous substance
that does not occur naturally or occurs at greater than natural background
levels." Wash.
Admin. Code § 173-340-200 (2001).
"'Environment' means any plant, animal, natural resource, surface water
(including underlying sediments), ground water, drinking water supply, land
surface (including tidelands and shorelands) or subsurface strata, or ambient
air within the state of Washington or under the jurisdiction of the state of
Washington." Id.
[FN64]. Wash.
Rev. Code § 70.105D.040(1).
[FN65]. Id.
§
70.105D.040(3).
[FN66]. Id.
§ 70.105D.030(2)(b).
[FN67]. See infra Part II.B.
[FN68]. See infra Part II.D.
[FN69]. Wash.
Rev. Code § 70.105D.040.
[FN70]. Strict liability is "[l]iability that does not
depend on actual negligence or intent to harm, but that is based on the breach
of an absolute duty to make something
safe." Black's Law Dictionary 926 (7th ed. 1999). Joint and several
liability is:
[l]iability that may be apportioned either
among two or more parties or to only one or a few select members of the group,
at the adversary's discretion. Thus, each liable party is individually
responsible for the entire obligation, but a paying party may have a right of
contribution and indemnity from nonpaying parties.
Id.
[FN71]. See infra notes 123-26 and accompanying text.
[FN72]. Wash.
Rev. Code § 70.105D.040(2).
[FN73]. Id.
§ § 70.105D.030(1)(b), .040(2).
[FN74]. Id.
§
70.105D.040(2).
[FN75]. Id.
§
70.105D.040(3).
[FN76]. Id.
[FN77]. Id. §
70.105D.040(3)(a)(i). MTCA does not define
"act of God."
[FN78]. Id.
§
70.105D.040(3)(a)(ii). MTCA does not define
"act of war."
[FN79]. Id.
§
70.105D.040(3)(a)(iii). This defense does not
apply if the potentially liable party had a direct or indirect contractual
relationship with the third party. Id.
[FN80]. Id.
§
70.105D.040(3).
[FN81]. Id.
§
70.105D.040(3)(b). This is subject to certain
restrictions. For example, the property owner must have made reasonable
inquiries into prior uses of the property to show that he or she had no reason
to know of the contamination. Id.
§
70.105D.040(3)(b)(i). Moreover, the court will
take into consideration the specialized knowledge of the buyer, the purchase
price for the property, the obviousness of the condition, and commonly known or
reasonably ascertainable information about the property. Id.
[FN82]. Id.
§ 70.105D.020(12)(b)(i). Involuntary acquisition, for the purposes of this
subsection, means acquiring the property "through bankruptcy, tax
delinquency, abandonment, or circumstances in which the government involuntarily acquires title." Id.
[FN83]. 42
U.S.C. § 9601(20)(D) (Supp. V 1999).
[FN84]. See, e.g., Lawrence P. Schnapf, CERCLA
and the Substantial Continuity Test: A Unifying Proposal for Imposing CERCLA
Liability Asset on Purchasers, 4 Envtl. Law. 435, 440 n.15 (1998) (stating that 42
U.S.C. § 9601(20)(D) "applies to state or
local governments that acquired title to a contaminated facility involuntarily
through ... eminent domain"); cf. Robert I. McMurry & David H. Pierce,
Environmental Remediation and Eminent Domain, C709 ALI-ABA 105, 117 (1992)
(stating that, at least in cases in which the government condemns property for
cleanup of contaminated property, it is "involuntarily" acquiring
property to protect public health and safety).
[FN85]. See Bird-Johnson
Corp. v. Dana Corp., 119 Wash. 2d 423, 427, 833 P.2d 375, 377 (1992).
[FN86]. Wash.
Rev. Code § 70.105D.030.
[FN87]. Wash.
Admin. Code § 173-340 (2001).
[FN88]. See infra Part
II.B.1.
[FN89]. See infra notes 101-03 and accompanying text.
[FN90]. Wash.
Admin. Code § 173-340-300(2)(a).
[FN91]. Wash.
Rev. Code § 70.105D.030(1)(a); see also Wash.
Admin. Code § 173-340-800.
[FN92]. Wash.
Admin. Code § 173-340-300(1).
[FN93]. Id.
§ 173-340-310.
[FN94]. Id.
§ 173-340-310(2). The DOE may defer to another governmental body or independent
contractor for the purposes of conducting the investigation, as long as the
other entity did not contribute to the hazardous condition at the site. Id. § 173-340-310(3).
[FN95]. Id.
§ 173-340-310(5)(a). "A site hazard assessment is an early study to
provide preliminary data regarding the relative potential hazard of the
site." Id.
§ 173-340-320(4).
[FN96]. Id. § 173-340-310(5)(b).
If a site requires emergency remedial action, the DOE must notify the
potentially affected area of the threat. Id.
§ 173-340-310(6)(a). "Emergency remedial action" is not defined by
the regulations.
[FN97]. Id.
§ 173-340-310(5)(c). An interim action may include an action necessary to (1)
reduce the threat to human health by eliminating or reducing "pathways for
exposure" to a hazardous substance, (2) correct a problem that may become
worse or more expensive if action is delayed, or (3) complete a site hazard
assessment, remedial investigation, or feasibility study, or provide for the
design of a cleanup action. Id.
§ 173-340-430(1).
[FN98]. Id.
§ 173-340-310(5)(d). A decision to undertake no further action may be
predicated upon a determination that no hazardous substance has been released,
no threat to human health exists, or any further action is more appropriately
undertaken under a different authority. Id.
[FN99]. Id.
§ § 173-340-120(3), -330. A site's appearance on the hazardous sites list is
not an implication that the parties associated with the site are subject to
MTCA liability. Id.
§ 173-340-330(5).
[FN100]. Id. § 173-340-500; see
also Wash.
Rev. Code § 70.105D.040 (2000).
[FN101]. See Wash.
Admin. Code § 173-340-700(5).
[FN102]. Id.
§
173-340-700(4)(a).
[FN103]. Id.
§
173-340-700(5). The Washington Administrative Code
outlines three basic methods to determine the proper level of remediation. Id. "Method A"
is used for sites for which cleanup is routine, or which involve relatively few
hazardous substances. Id.
§
173-340-700(5)(a). "Method B" is the
standard method used for all sites, unless one of the conditions applicable to
Methods A or C exists. Id.
§
§ 173-340- 700(5)(b), -705(1). "Method
C" is a conditional method, applicable if compliance with Methods A or B
is impossible or will cause greater environmental harm. Id. §
173-340-700(5)(c). Method C is also applicable to
certain industrial properties. Id.;
see also id. § 173-340-745 (setting forth soil cleanup standards for industrial
properties).
[FN104]. Wash.
Rev. Code § 70.105D.020(21).
[FN105]. Id.
[FN106]. Wash.
Admin. Code § 173-340-510(3)(b).
[FN107]. Id.
§ 173-340-520(2).
[FN108]. Id.
§ 173-340-520(2)(b).
[FN109]. Id.
§ 173-340-540. The DOE generally issues the enforcement order either after it
has sent a negotiation letter or else concurrently, in the case of an
emergency. Id.
[FN110]. Id.
§ 173-340-530(1).
[FN111]. Id.
[FN112]. Id.
[FN113]. Id.
§
173-340-510(4).
[FN114]. Id.
§
§ 173-340-510(2), -515.
[FN115]. Id. § 173-340-520; see
also Wash.
Rev. Code § 70.105D.040(4) (2000).
[FN116]. Wash.
Admin. Code § § 173-340-520(1)(v), (viii).
[FN117]. Wash.
Rev. Code § 70.105D.040(4)(a); Wash.
Admin. Code § 173- 340-520(f).
[FN118]. Wash.
Admin. Code § 173-340-515.
[FN119]. Id.
[FN120]. Id. §
173-340-515(5); see also 24 Timothy H. Butler, Environmental Law
and Practice, in Washington Practice, § 15.26 (1997).
[FN121]. Wash.
Admin. Code § 173-340-300(4).
[FN122]. Id.
§
§ 173-340-310(4), -515(4).
[FN123]. Wash.
Rev. Code § 70.105D.050(3) (2000).
[FN124]. Costs of
direct remedial activities include, for example, the payment of staff for work
on the site, the cost of any travel related to the site, costs incurred
publishing documents with respect to the site, the purchase or rental of any
equipment necessary for remediation of the site, and the cost of work on the
site that must be contracted out. Wash.
Admin. Code § 173-340-550(2)(a).
[FN125]. Support costs include, for example, costs of any
facilities, personnel, and administrative support that are indirectly related
to the remediation of the site. Id.
§
173-340-550(2)(b)-(c).
[FN126]. Id.
§
173-340-550(2).
[FN127]. Wash.
Rev. Code § 70.105D.050(1).
[FN128]. Id.
[FN129]. Id.
§ 70.105D.080.
[FN130]. Id.
§
70.105D.020 (14). "Person" is defined
as an "individual, firm, corporation,
association, partnership, consortium, joint venture, commercial entity, state
government agency, unit of local government, federal government agency, or
Indian tribe." Id.
[FN131]. Id.
§ 70.105D.080.
[FN132]. Wash.
Admin. Code § 173-340-545(2) (2001).
[FN133]. Id.
§
173-340-545(2)(c)(i).
[FN134]. Id.
§
173-340-545(2)(c)(ii).
[FN135]. Id.
§
173-340-545(2)(c)(iii). The remedial action may
also be "substantially
equivalent" if it has actually been conducted by the DOE itself, or if it
is being conducted under an order or decree, and the requirements of the decree
have been fulfilled. Id.
§
173-340-545(2)(a)-(b).
[FN136]. See supra notes 75-81 and accompanying text.
[FN137]. Wash.
Const. art. I, § 3.
[FN138]. U.S.
Const. amend. XIV, § 1.
[FN139]. Olympic
Forest Prods., Inc. v. Chaussee Corp., 82 Wash. 2d 418, 422, 511 P.2d 1002,
1005 (1973) (citing Grannis
v. Ordean, 234 U.S. 385, 394 (1914), Mullane
v. Cent. Hanover Bank & Trust Co., 339 U.S. 306, 314 (1950), and Armstrong
v. Manzo, 380 U.S. 545, 552 (1965)).
[FN140]. Id.
at 428, 511
P.2d at 1008. In determining the level of process
that is due, the court will balance the interest to be protected, the risk of
deprivation of that interest by the government's acts, and the government's
interest in maintaining the procedure. Silver
Firs Town Homes, Inc. v. Silver Lake Water Dist., 103 Wash. App. 411, 425, 12
P.3d 1022, 1029 (2000).
[FN141]. Zinermon
v. Burch, 494 U.S. 113, 125 (1990).
[FN142]. Mathews
v. Eldridge, 424 U.S. 319, 332 (1976).
[FN143]. Zinermon,
494 U.S. at 125.
[FN144]. Carey
v. Piphus, 435 U.S. 247, 259-60 (1978) (quoting Fuentes v.
Shevin, 407 U.S. 67, 81 (1972)). Whether
procedural due process protections are implicated in a given case depends upon
whether the interest in question falls within the ambit of "life, liberty,
or property." Morrissey
v. Brewer, 408 U.S. 471, 481 (1972). Neither the Washington State nor the United States
Constitutions define exactly what that phrase encompasses. The United States
Supreme Court has made it clear, however, that the scope of "property
interests" is broader than simply the ownership of money, real estate, or
chattel. Bd.
of Regents of State Colls. v. Roth, 408 U.S. 564, 571-72 (1972). Similarly, "liberty" means something more than
simply freedom from physical confinement. Id.
at 572 n.11. Moreover, for purposes of procedural
due process, property interests "are not created by the constitution but
are reasonable expectations of entitlement derived from independent sources
such as state law." Mission
Springs, Inc. v. City of Spokane, 134 Wash. 2d 947, 962 n.15, 954 P.2d 250, 257
n.15 (1998) (citing Roth,
408 U.S. at 577). Thus, a property interest may
be created by a state statute or statutory scheme. See Mathews,
424 U.S. at 332; Mission
Springs, 134 Wash. 2d at 963, 954 P.2d at 257
(citing Bateson
v. Geisse, 857 F.2d 1300, 1304-05 (9th Cir. 1988)).
[FN145]. 424
U.S. 319 (1976).
[FN146]. Id.
at 335 (citing Goldberg
v. Kelly, 397 U.S. 254, 263-71 (1970)).
[FN147]. Id.
[FN148]. Zinermon,
494 U.S. at 127-28 (citing Cleveland
Bd. of Educ. v. Loudermill, 470 U.S. 532, 542 (1985); Parham
v. J.R., 442 U.S. 584, 606- 07 (1979); Memphis
Light, Gas & Water Div. v. Craft, 436 U.S. 1, 18 (1978); Goss
v. Lopez, 419 U.S. 565, 579 (1975); Wolff
v. McDonnell, 418 U.S. 539, 557-58 (1974); Fuentes,
407 U.S. at 80-84; Goldberg,
397 U.S. at 264). Once a court has determined
whether the protections of procedural due process apply, it must then determine
exactly what process is due. Loudermill,
470 U.S. at 541.
Again, neither the Washington State
nor the United States Constitutions dictate exactly what level or character of
due process must be afforded in a given situation. The concept of due process
is "flexible," and will vary according to the demands of the
particular situation. Mathews,
424 U.S. at 334 (quoting Morrissey,
408 U.S. at 481). The determination of what
process is due depends upon what rights are at stake and entails "'a
determination of the precise nature of the government function involved as well
as of the private interest that has been affected by governmental action."'
Morrissey,
408 U.S. at 481 (quoting Cafeteria
& Rest. Workers v.
McElroy, 367 U.S. 886, 895 (1961)). The same
procedural rule won't necessarily satisfy the requirements of due process in
every context; "[t] hus, procedures adequate to determine a welfare claim
may not suffice to try a felony charge." Bell
v. Burson, 402 U.S. 535, 540 (1971).
[FN149]. Goldberg,
397 U.S. at 267 (citing Armstrong
v. Manzo, 380 U.S. 545, 552 (1965)).
[FN150]. Bell,
402 U.S. at 542.
[FN151]. 402
U.S. 535 (1971).
[FN152]. Id.
at 535-36.
[FN153]. Id.
at 541-42.
[FN154]. 397
U.S. 254 (1970).
[FN155]. Id.
at 267-68.
[FN156]. Olympic
Forest Prods., Inc. v. Chaussee Corp., 82 Wash. 2d 418, 422,
511 P.2d 1002, 1005 (1973) (citing Armstrong
v. Manzo, 380 U.S. 545, 552 (1965); Mullane
v. Cent. Hanover Bank & Trust Co., 339 U.S. 306, 314 (1950); Grannis
v. Ordean, 234 U.S. 385, 394 (1914)). In Washington, the court
will balance the interest to be protected, the risk of deprivation of that
interest by the government's acts, and the government's interest in maintaining
the procedure. See, e.g., Silver
Firs Town Homes, Inc. v. Silver Lake Water Dist., 103 Wash. App. 411, 425, 12
P.3d 1022, 1029 (2000).
[FN157]. Olympic
Forest Prods., 82 Wash. 2d at 422, 511 P.2d at 1005.
[FN158]. Id.
at 428, 511 P.2d at 1008.
[FN159]. 82
Wash. 2d 418, 511 P.2d 1002 (1973).
[FN160]. Id.
at 423-24, 511 P.2d at 1006 (citing Joint
Anti-Fascist Refugee Comm. v. McGrath, 341 U.S. 123, 163 (1951) (Frankfurter, J., concurring)).
[FN161]. Thus far, very few jurisdictions have considered the
problem at all. A majority in favor of admitting the evidence has emerged. See,
e.g., Redev. Agency
v. Thrifty Oil Co., 5 Cal. Rptr. 2d 687, 689 n.9 (Cal. Ct. App.1992); State
Dep't of Health v. The Mill, 887 P.2d 993, 1008 (Colo. 1994); N.E. Econ.
Alliance, Inc. v. ATC P'ship, 776 A.2d 1068, 1080 (Conn. 2001); Finkelstein
v. Dep't of Transp., 656 So.2d 921, 922 (Fla. 1995);
City
of Olathe v. Stott, 861 P.2d 1287, 1290 (Kan. 1993);
State
v. Hughes, 986 P.2d 700, 703 (Or. Ct. App. 1999);
State
v. Brandon, 898 S.W.2d 224, 226-27 (Tenn. Ct. App. 1994). But see Dep't
of Transp. v. Parr, 633 N.E.2d 19 (Ill. Ct. App. 1994); Aladdin,
Inc. v. Black Hawk County, 562 N.W.2d 608, 615 (Iowa 1997).
[FN162]. Aladdin,
562 N.W.2d at 615.
[FN163]. 562
N.W.2d 608 (Iowa 1997).
[FN164]. Id.
at 610.
[FN165]. Id.
[FN166]. Id.
at 615.
[FN167]. Id.
at 615-16.
[FN168]. See id. at
615.
[FN169]. Id.
[FN170]. Id.
at 615-16.
[FN171]. Id.
at 615.
[FN172]. Id.
[FN173]. Id.
The Aladdin court was also concerned that valuation of contaminated property
would be problematic due to the difficulty of locating comparable contaminated
property, and that the fact-finder would be required to speculate as to the
effect of the contamination upon the property's value. Id. at 616.
[FN174]. 633
N.E.2d 19 (Ill. Ct. App. 1994).
[FN175]. Id.
at 22.
[FN176]. Id.
at 20.
[FN177]. Id.
at 22-23.
[FN178]. Id.
at 22.
[FN179]. Id.
[FN180]. Id.
at 23.
[FN181]. Id.
at 22.
[FN182]. See, e.g., Redev. Agency v. Thrifty Oil Co., 5 Cal. Rtpr.
2d 687, 689 n.9 (Cal. Ct. App. 1992); City
of Olathe v. Stott, 861 P.2d 1287, 1290 (Kan. 1993);
State
v. Hughes, 986 P.2d 700, 703 (Or. Ct. App. 1999).
[FN183]. 986
P.2d 700 (Or. Ct. App. 1999).
[FN184]. Id.
at 703.
[FN185]. Id.
at 701.
[FN186]. Id.
at 702. The court did not discuss any applicable
environmental remediation statute in Oregon.
[FN187]. "Relevant evidence" means "evidence having
any tendency to make the existence of any fact that is of consequence to the
determination of the action more probable or less probable than it would be
without the evidence." Id.
at 703.
[FN188]. Id.
[FN189]. Id.;
see also Redev. Agency
v. Thrifty Oil Co., 5 Cal. Rptr. 2d 687, 689 n.9 (Cal. Ct. App. 1992) (stating that remediation issue was properly before jury
as a property characteristic that affected value of land); City
of Olathe v. Stott, 861 P.2d 1287, 1290 (Kan. 1993)
(stating that evidence of contamination should be admissible in eminent domain
proceeding because a purpose of an eminent domain proceeding is to determine fair
market value of subject property and contamination affects that value).
[FN190]. 656
So.2d 921 (Fla. 1995).
[FN191]. Id.
at 924.
[FN192]. See Dep't
of Transp. v. Finkelstein, 629 So.2d 932, 932 (Fla. Ct. App. 1993).
[FN193]. Finkelstein
v. Dep't of Transp., 656 So.2d 921, 922 (Fla. 1995).
[FN194]. See id.
at 924:
Holding contamination to be relevant to the
market value of property in an eminent domain valuation proceeding is
consistent with our decision in Florida
Power & Light Co. v. Jennings, 518 So.2d 895 (Fla. 1987), in which we held that "any factor including public
fear which impacts on the market value of land taken for a public purpose may
be considered to explain the basis for an expert's valuation opinion."
As noted
previously, Washington
courts do not follow this reasoning. See
State
v. Evans, 96 Wash. 2d 119, 127, 634 P.2d 845, 849 (1981), opinion amended, 649
P.2d 633 (1982).
[FN195]. Finkelstein,
656 So.2d at 924. The court defined
"stigma" as "the
reduction in value caused by contamination resulting from the increased risk
associated with the contaminated property. In sum, many prospective buyers are
afraid of the financial risk associated with contaminated or even previously contaminated properties and would
therefore pay less for the property." Id. (internal quotation marks omitted).
[FN196]. Id.
[FN197]. Id.
[FN198]. Id. Ultimately, however, the Finkelstein court concluded
that the evidence of contamination was not admissible in the case before it, as
there was not a sufficient factual basis for the state expert's valuation
opinion. Id.
at 925. Because there was no factual evidence in the record upon which to base
the conclusion that the property's value had actually been compromised by the
alleged environmental contamination, the landowner was entitled to the fair
market value of the property without respect to contamination. Id.
[FN199]. 776
A.2d 1068 (Conn. 2001).
[FN200]. Id.
at 1072-73. The trial court had held that the
contamination evidence was not admissible. N.E.
Econ. Alliance, Inc. v. ATC P'ship, No. CV 940049248S, 1998 WL 197632, *15
(Conn. Super. April 16, 1998). During the pendency of the parties' appeal, the Connecticut legislature
amended its eminent domain statute to provide that evidence of environmental
contamination is admissible to determine just compensation. ATC
P'ship, 776 A.2d at 1076 (citing Public Acts
2000, No. 00-89, entitled "An Act Concerning Fair Market Value Of
Brownfields"). However, the ATC Partnership court did not decide whether
the new provision applied retroactively, but instead based its determination on
"traditional constitutional principles of just compensation." Id.
[FN201]. ATC
P'ship, 776 A.2d at 1080.
[FN202]. Id.
at 1081.
[FN203]. Cf. In
re City of Medina, 69 Wash. 2d 574, 578, 418 P.2d 1020, 1023 (1966).
[FN204]. State
v. Evans, 96 Wash. 2d 119, 127, 634 P.2d 845, 849 (1981), opinion amended, 649
P.2d 633 (1982).
[FN205]. Id.
[FN206]. See supra
notes 49-52 and accompanying text.
[FN207]. See supra notes 49-52 and accompanying text.
[FN208]. See supra notes 101-28 and accompanying text.
[FN209]. Butler,
supra note 120, § 15.57.
[FN210]. See Robert I. McMurry, Treatment of Environmental
Contamination in Eminent Domain Cases, C975 ALI-ABA 237, 247 (1995) (stating
that "consultants will concede that environmental investigations are more
than a little like handicapping horse races: there is some science involved and
some things we can put into statistics, but a big part of the equation is
uncertain, unpredictable, incalculable, and perhaps even unknowable").
[FN211]. 7A Julius Sackman, Nichols on Eminent Domain §
13B.03[2][i][ii] (3d Ed. Rev. 2000).
[FN212]. Sackman, supra note 211, § 13B.03[2][i][iii]; Amy Grigham
Boulris, Dealing with Contaminated
Land from the Condemnee's
Perspective, C975 ALI-ABA 197, 203 (1995).
[FN213]. See Sackman,
supra note 211, § 13B.04[2].
[FN214]. See Sackman, supra note 211, § 13B.04[2].
[FN215]. See Sackman, supra note 36, § 12.02[1], at 12-72.
[FN216]. See Aladdin,
Inc. v. Black Hawk County, 562 N.W.2d 608, 616
(Iowa 1997) ("Properties with
contamination are hard to compare because they involve multiple varieties of
contamination of varying concentrations and require assorted methods of
cleanup. The commission, judge, or jury required to determine 'just
compensation' would likely be compelled to speculate as to the damages.").
See also Robert I. McMurry & David H. Pierce, Environmental Contamination
and Its Effect on Eminent Domain, C791 ALI-ABA 133, 162. Although locating
similar property may not, in all cases, be impossible, considerations of
judicial economy suggest it would be inefficient to always attempt to do so.
[FN217]. In
re City of Medina, 69 Wash. 2d 574, 578, 418 P.2d 1020, 1022- 23 (1966).
[FN218]. Id.
[FN219]. S ee Sackman,
supra note 36, § 12.02[1].
[FN220]. See supra notes 213-18 and accompanying text.
[FN221]. For a discussion of novel valuation methodologies that
may alleviate the problem to some degree, see McMurry & Pierce, supra note
216, at 165-69 (suggesting that these novel alternatives are still somewhat
unsatisfactory); see also Sackman, supra note 211, § 13B.04[2] (listing newer
valuation methods but noting that "[t]he development of techniques for
valuing contaminated properties is still in its infancy") (internal
quotation marks omitted).
[FN222]. See, e.g., Finkelstein
v. Dep't of Transp., 656 So.2d 921, 924
(Fla. 1995) (citing Fla.
Power & Light Co. v. Jennings, 518 So.2d 895 (Fla. 1987)).
[FN223]. See supra notes 193-94 and accompanying text.
[FN224]. See supra notes 193-94 and accompanying text.
[FN225]. See, e.g., State
v. Evans, 96 Wash. 2d 119, 127, 634 P.2d 845, 849 (1981), opinion amended, 649
P.2d 633 (1982); Pac.
N.W. Pipeline Corp. v. Myers, 50 Wash. 2d 288, 290, 311 P.2d 655, 656 (1957).
[FN226]. See supra note 144 and accompanying text.
[FN227]. See supra note 148 and accompanying text.
[FN228]. 424
U.S. 319 (1976).
[FN229]. See supra note 33 and accompanying text.
[FN230]. See supra notes 145-47 and accompanying text.
[FN231]. See supra Part II.B.
[FN232]. See supra Part II.A.
[FN233]. See supra note 70 and accompanying text.
[FN234]. See supra notes 129-35 and accompanying text.
[FN235]. See supra
notes 149-55 and accompanying text.
[FN236]. See, e.g., Dep't
of Transp. v. Parr, 633 N.E.2d 19, 22 (Ill. Ct. App. 1994); Aladdin,
Inc. v. Black Hawk County, 562 N.W.2d 608, 615 (Iowa 1997).
[FN237]. 633
N.E.2d 19, (Ill. Ct. App. 1994).
[FN238]. Id.
at 22-23.
[FN239]. Id.
[FN240]. See Car
Wash Enters. v. Kampamos, 74 Wash. App. 537, 544, 874 P.2d 868, 873 (holding that nothing in MTCA prohibits private parties
from allocating risk amongst themselves, though emphasizing that such a private
agreement has no effect on liability as to the state); cf. Boeing
Co. v. Aetna Cas. & Sur. Co., 113 Wash. 2d 869, 887, 784 P.2d 507, 516
(1990) (holding that response costs under CERCLA
are "damages" within the meaning of an insurance policy); see also Olds-Olympic,
Inc. v. Comm. Union Ins. Co., 129 Wash. 2d 464, 473, 918 P.2d 923, 927 (1996) (stating that the holding in Boeing applies to MTCA).
[FN241]. Wash.
Rev. Code § 70.105D.050 (2000).
[FN242]. See supra notes 129-35 and accompanying text.
[FN238]. Id.
at 22-23.
[FN239]. Id.
[FN240]. See Car
Wash Enters. v. Kampamos, 74 Wash. App. 537, 544, 874 P.2d 868, 873 (holding that nothing in MTCA prohibits private parties
from allocating risk amongst themselves, though emphasizing that such a private
agreement has no effect on liability as to the state); cf. Boeing
Co. v. Aetna Cas. & Sur. Co., 113 Wash. 2d 869, 887, 784 P.2d 507, 516
(1990) (holding that response costs under CERCLA
are "damages" within the meaning of an insurance policy); see also Olds-Olympic,
Inc. v. Comm. Union Ins. Co., 129 Wash. 2d 464, 473, 918 P.2d 923, 927 (1996) (stating that the holding in Boeing applies to MTCA).
[FN241]. Wash.
Rev. Code § 70.105D.050 (2000).
[FN242]. See supra notes 129-35 and accompanying text.
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