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By Paul Munter, René Sacasas, and Elaine Garcia
The problems of environmental cleanup costs are not restricted to
large chemical and petroleum companies. Many small businesses now have
to face these predicaments. The authors explain the background and provide
guidance on accounting and disclosure requirements for entities faced with
this dilemma. A sidebar presents an outline of AcSEC's proposed guidance
on accounting when the threat of litigation, claim, or assessment results
in the decision to take remedial action. Have you heard the story about the local florist who bought a piece
of property for $80,000 because it would be the perfect place for his new
store? Turns out, the property was once used as a service station, and
a local ordinance requires that property converted into alternate use must
first be remediated. The cost to remove the underground gasoline tanks,
which were abandoned after the service station closed, and to remediate
the soil came to $600,000‹all of which was to be paid by the florist. How about the local automobile dealer who had been paying a registered
company to remove and dispose of the used motor oil? Turns out, the hauler
did not properly dispose of the motor oil and all the haulers' customers
were required to help pay for the cleanup efforts. We often hear accountants say, "Oh, that talk about environmental
liabilities is just a subject for the big companies who operate in polluting
industries." In today's environmentally sensitive era, that is not
true. Companies big and small, in all industries‹from the two cases just
cited, to the small municipality that operates a landfill, to the local
dry cleaner, to the bank who financed property that subsequently had to
be cleaned up‹are faced with paying for and, consequently, accounting for
the cost of environmental cleanup. Further, because the problem is so pervasive,
it can be an issue in the financial statements regardless of whether the
financial statements are prepared on a GAAP basis or an OCBOA basis. Environmental regulation in the U.S. began in earnest in the late 1950s
as legislation was passed at the Federal, state, and local levels to decrease
the nation's water and air pollution. During the following decade, significant
environmental legislation was enacted in response to public demands. This
was followed with the creation of the Environmental Protection Agency (EPA)
which was created in 1970 to enforce the Federal government's legislation
regulating air and water pollution, solid waste disposal, water supply,
pesticide and radiation control, and ocean dumping. Subsequent legislation
has expanded the EPA's mandate to include other pollution problems such
as toxic waste disposal and acid rain. Environmental regulation continued to evolve significantly in the 1980s
through the present as politicians and judges reacted to society's efforts
to refine the rules to balance the preservation of the environment with
the growth demands of our society. These laws typically address three categories
of pollution: air, water, and solid waste disposal. However, some pollution
problems are so comprehensive that they may affect all elements of the
environment. The Clean Air Act, originally passed in 1963, was amended in 1990 to
focus on issues such as acid rain, urban smog, airborne toxins, ozone-depleting
chemicals, and other problems. These recent amendments had a substantial
impact on businesses not normally considered polluters. Now, paint shops
and bakeries can be labeled as polluters because the definition of a major
polluter was changed. Utilities and other factories also have been affected
by a new cap on sulfur dioxide emissions‹a contributor to acid rain. Interestingly,
however, the amendment allowed companies whose emissions were cleaner than
required by law to sell their rights to emit more sulfur dioxide to other
companies. This has lead to a new commodity for sale‹so-called pollution
credits. An example of the financial implications of these laws can be seen with
asbestos. As a toxic air pollutant, asbestos is regulated by the EPA. As
a known carcinogen, liability can result from the emission of its fibers.
Its presence can impose a serious financial obligation on property owners
and, thus, should be disclosed to potential buyers. Although the use of
asbestos in new construction has been banned since the 1970s, many older
structures still have asbestos-containing materials, such as ceiling tiles
and insulation on boiler systems, elevator shafts, fan units, and hot water
tanks. Federal requirements only stipulate the removal of asbestos in schools
or where existing asbestos results in airborne levels exceeding Federal
standards. It must be removed, however, before the demolition of a building
or if the demolition debris could be classified as hazardous waste. If
it is not removed, all the demolition debris can be classified as hazardous
waste, which will significantly increase the cost of disposal. Further,
it often is necessary to remove the asbestos when major reconstruction
of the facilities takes place. This could significantly increase the anticipated
cost of a construction project if this cost is not considered in planning
the project. With the enactment of the Clean Water Act in 1972, control of water
pollution was established at the Federal level. This law also required
industries discharging wastes into waterways to install the best available
water pollution control technology. These dischargers were also required
to obtain permits specifying the pollutants and amounts allowed to be discharged.
The wetlands provision of this act has enormous significance for property
owners. Wetlands‹which provide essential habitats to a variety of animal
life and 35% of endangered species, moderate effects of flood waters, and
control water pollution‹have only gained recognition and protection recently.
A permit is required to construct in a designated wetland area and is usually
not granted unless the applicant can prove the wetlands will not be harmed.
Some permits are granted on the condition the wetlands will be restored
or recreated in another location, but equal to or greater than the proposed
loss of wetlands. This can be an expensive undertaking. Therefore, a prospective
buyer should thoroughly investigate the possibility that the property or
adjacent area is considered a wetland. The water pollution and wetlands provision can have far-reaching implications.
Companies, both small and large, in industries as diverse as construction,
agriculture, dry cleaning, mining, and theme/ amusement parks have been
affected. The safe disposal of garbage and other waste has always been an ecological
concern. Proper disposal is becoming more difficult as the population and
our production of wastes increase. Hazardous waste disposal is a comprehensive pollution problem whose
effects on land, drinking water, and human health will span generations.
After encountering the problems created by open chemical dumping at places
such as Love Canal, the EPA was authorized to prevent, restrict, or stop
the manufacture and use of chemicals that present an unreasonable risk
of injury to humans or the environment. Manufacturers also must obtain
a permit for the storage or transfer of hazardous wastes. Underground storage tanks represent yet another potential problem. Currently
tanks are constructed of steel with corrosion protection, but this was
not always the case. Many older tanks on properties formerly used as service
stations and fuel oil distributors are developing leaks after 10 to 20
years of use. The material, once leaked out, can go undetected until soil
and groundwater are contaminated. The EPA enacted regulations in 1988 that
require leak testing, installation of corrosion protection and leak detection
systems, and insurance against leakage. While the cost of these preventive
measures can be significant, it pales in comparison to the cost of a cleanup
if the old tanks have leaked. Congress created the Comprehensive Environmental Response Compensation
and Liability Act (CERCLA) or Superfund in 1980 to manage the growing problem
of uncontrolled or abandoned hazardous waste-disposal sites. Under Superfund,
the EPA identifies and assesses sites where hazardous substances have been
spilled, stored, or abandoned. Sites are subsequently ranked after consideration
of a number of factors, including the potential number of people exposed,
types of exposure, and risk of contamination of drinking water. Sites with
the highest rankings receive priority attention from the Federal and/or
state government to facilitate cleanup. The cleanup process may include
excavating and disposing of some surface soil at a cost of a few thousand
dollars. It may involve the more expensive procedure of pumping groundwater
through filter systems and returning it to the aquifer, as well as removing
and disposing of extensive quantities of soil. In the latter case, the
cost of cleanup can quickly run into millions of dollars for even a small
site. When a site requires cleanup, the EPA demands that the owner and all
other parties responsible for contaminating the site, including the owner
or operator of the contaminated site, transporter of the wastes deposited
at the site, or owner of the wastes, undertake the cleanup effort (including
responsibility for the costs of the cleanup). If the parties refuse, the
EPA has the authority to clean up the site and demand payment plus treble
damages from the responsible parties. Accordingly, noncompliance with such
an EPA demand presents very substantial economic risks to companies. This
liability has been expanded to include subsequent purchasers of the property
who did not perform sufficient "due diligence" checks on its
history, financial institutions lending money to the responsible persons,
and creditors foreclosing on the property. All prospective purchasers and successors in interest, such as foreclosing
creditors, must evaluate carefully the potential environmental liabilities
of each parcel of property they plan to acquire since they may be held
financially and legally responsible for future problems. If the land is
targeted for cleanup by the EPA, it can request the current owner to commence
a cleanup operation, even if it was not responsible for the damage. Imagine
the chagrin of a creditor who forecloses on a piece of property that, unfortunately,
was a hazardous waste site. The EPA can order the lender to clean up the
site. If the creditor refuses, the EPA will remove the contamination and
sue the creditor for the cost of the cleanup. In some cases the corporate
officers may be held personally responsible. The issue of this expanded liability remains cloudy, particularly with
regard to lender liability. The EPA has proposed to eliminate cleanup liability
for lenders who cease activities on the property or sell the site within
six months after takeover. Foreclosures and purchases of properties with
known or possible hazardous waste problems nevertheless should be undertaken
cautiously and with the supervision of an attorney and other professionals
to limit potential liability. Other defenses to liability for the cleanup of contaminated property
include proving the contamination was caused solely through an act of God,
an act of war, or an act or omission of a third party. The third party,
however, may not be an employee or agent of the defendant or one whose
act or omission occurs in connection with a contractual arrangement (including
land contracts) with the defendant. There is also an "innocent landowner" exception to the legislation's
requirement that no privity of contract exist between the defendant and
the party responsible for the contamination for the defendant to invoke
third party defense. This exception may be established by proving the defendant
acquired the property subsequent to the occurrence of the contamination
at the site, the contamination was unknown when the site was acquired,
due care was exercised with the hazardous materials involved, and the defendant
took precautions against foreseeable acts or omissions by third parties.
To establish the requisite legal foundation that the defendant had no prior
knowledge of the contamination, the defendant must have appropriately inquired
into the previous ownership and uses of the property. Properly assessing the property for potential environmental concerns
and risks through environmental due diligence is crucial to the "innocent
landowner" defense. An initial evaluation will involve a site inspection
to uncover potential environmental hazards, including underground storage
tanks, asbestos materials, and wetlands, a comprehensive background investigation
of the property's history, and a review of records for noncompliance of
regulations. If no evidence of potential problems is discovered, more thorough
and expensive research may not be necessary. If, however, the above inquiries and investigations find evidence of
problems, these must be identified and resolved. Chemical testing of samples
from the soil, water, air, or suspected materials should be conducted.
An electrical conductivity/resistivity survey may be performed to detect
underground storage tanks or drums. Hydrostatic leak tests will reveal
any leaking. These tests may be expensive, but not when compared with the
costs if contamination is discovered in the future. After a number of industrial accidents were published in the press,
in 1986 Congress amended the Superfund with Community Right to Know requirements.
These included emergency planning, notification of spills and accidents
involving hazardous materials, and disclosure by industry to the community
about the presence and amounts of listed chemicals released into the surrounding
area. These regulations have motivated corporations to reduce their emissions
to avoid public scrutiny. Further, a duty to disclose the presence of these
listed chemicals to potential buyers, tenants, or employees may also exist.
The current accounting and reporting guidance for the accrual and disclosure
of environmental liabilities exists in several sources within the GAAP
hierarchy. The applicable documents include the following: * SFAS No. 5, Accounting for Contingencies * FASB Interpretation No. 14, Reasonable Estimation of the Amount
of a Loss * FASB Interpretation No. 39, Offsetting of Amounts Relating to Certain
Contracts * EITF Issue No. 89-13, Accounting for the Cost of Asbestos Removal
* EITF Issue No. 90-8, Capitalization of Costs to Treat Environmental
Contamination * EITF Issue No. 93-5, Accounting for Environmental Liabilities * SOP 94-6, Disclosure of Certain Significant Risks and Uncertainties
In June 1995, AICPA's AcSEC issued a proposed SOP, Environmental
Remediation Liabilities, whose purpose is to "narrow the manner
in which existent authoritative accounting literature is supplied by entities
to the specific circumstances of recognizing, measuring, and disclosing
environmental remediation liabilities." The exposure draft also contains
a discussion of major Federal legislation dealing with pollution control
laws and environmental cleanup laws and the need to also consider state
and non-Federal laws and regulations. The proposal closes with a section
on how to audit environmental remediation liabilities. An accompanying
sidebar briefly explains the contents of the proposal, whose deadline for
comment was October 31, 1995. In addition to these standards, SEC registrants must be cognizant of
the provisions of SAB No. 92, Accounting and Disclosures Relating to
Loss Contingencies. Conceptually, the accounting and reporting requirements
of environmental liabilities or contingencies are no different than those
for other liabilities. Because of the significant exposure that exists,
however, and the difficulty in estimating the potential costs, it is often
difficult to evaluate adequately the accounting and disclosure requirements
applicable to environmental issues. Let us consider the accounting requirements
and then examine the disclosure provisions of these documents. As is the case in evaluating other contingencies, the primary guidance
can be found in SFAS No. 5. Paragraph 8 of SFAS No. 5 specifies that a
loss contingency should be accrued when the loss is deemed to be both probable
(defined as the future events are likely to occur) and reasonably estimable.
While the provisions of SFAS No. 5 appear to provide adequate guidance
in evaluating many contingent liabilities, when applied to environmental
liabilities companies are faced with more difficult problems because of
changing laws and regulations, changing technologies, and the legal environment
(joint and several liability). Thus, given today's accounting and reporting environment, it would seem
all companies (regardless of whether publicly or privately held and regardless
of whether they use GAAP or OCBOA reporting principles) need to carefully
evaluate their operations to determine whether any environmental exposure
exists. If the company has identified an existing environmental problem
for which it may be required to participate in the cleanup, the company
should determine if an accrual is appropriate unless it can clearly show
that the cost will not be material to the entity. On this point, SAB No.
92 argues that accruing a rough estimate now (which may need to be significantly
revised later) is a better accounting approach than waiting until more
precise information is available later. The fundamental point raised by the SEC is that the entity has a liability
and, while it may not know the precise amount, it is probable the ultimate
amount will exceed $0 (or the entity's materiality threshold). When an
entity argues it does not yet have a reasonable estimate, it will accrue
no provision, thus reporting a liability of $0. Even the imprecise information
shows the company's liability is larger than $0; thus, the SEC's point
is that the accrual of some amount is a better representation of the company's
financial position than is no accrual. While it can be argued that SAB No. 92 is applicable only to SEC registrants,
the fact remains the SEC's logic is perfectly consistent with the provisions
of SFAS No. 5. It is perhaps when the estimates of liability are the least precise
that SOP 94-6 will come into play. That statement, which is effective for
years ending after December 15, 1995, requires disclosure when it is reasonably
possible that estimates included in financial statements will change in
the near term and the change could be material to the financial statements.
The EITF's conclusions in Issue 93-5 address another very important
component of the estimation issue. While some of the costs might be covered
by other parties (such as other participants or insurance carriers), the
entity must separately evaluate the liability and any recoveries. Thus,
if it is probable the entity will incur costs, the liability is probable
and, thus, accruable. If recovery is also probable, then the expense can
be reduced by the probable recovery. While the expense can be reduced for probable recoveries in accordance
with EITF Issue 93-5 (i.e., the income statement treatment), the provisions
of Interpretation No. 39 would lead to the conclusion that the asset and
liability need to be separately reported in the balance sheet. Thus, even
if no material cost (net of recoveries) is expected to be incurred by the
entity, the provision may still need to be accrued since the company may
have both a material liability and a material asset to report in the balance
sheet. The foregoing conclusions argue for earlier accrual of potential environmental
matters and for "grossing up" in the balance sheet. What of the
issue of disclosure? Of particular concern to many entities is whether
disclosure needs to be provided on a site-specific basis. The argument
that many companies will make is that providing such specific disclosures
may trigger legal and other costs that would not have been otherwise incurred.
Again, the practice applicable to SEC registrants may be instructive.
Environmental cleanup can be segregated, broadly, into two groups: 1) Superfund
sites (or other sites where the cleanup is conducted under the direction
or authority of a Federal or state agency) and 2) other cleanup sites.
Entities involved in Superfund cleanups are listed by the governmental
agency. Thus, it can be argued the company's involvement in that cleanup
effort is already a matter of public record. Following this argument, many
in the profession would suggest that site-specific disclosure would be
called for when an entity is involved in Superfund cleanup site(s). Conversely, however, if the company has discovered an environmental
problem following its own due diligence procedures and has cleaned up the
site on its own authority, the information is not a matter of public record.
For these types of cleanup efforts, a strong argument can be made that
an aggregate disclosure is appropriate in discussing such sites. If a company fails to properly report environmental liabilities, the
responsible parties expose themselves to future claims that the financial
statements did not have adequate disclosure of all material information.
Conversely, though, if the financial statements do contain specific
presentation of the exposure for environmental cleanup, it is possible
that outsider parties who might not have been aware of these problems may
be able to more readily press claims for the cost of cleanup plus additional
damages. Given this dilemma, it appears that due diligence is the operative word.
Management must apply appropriate due diligence when it acquires property,
when it monitors its operations and disposal methods, and when it discovers
an environmental problem. While companies may seek to avoid the accrual or disclosure requirements,
it is unquestionably true that these issues can only become more significant
in the future. Thus, it behooves companies to adequately address the accounting
and disclosure implications of potential monetary consequences from today's
environmentally-sensitive society. * Paul Munter, PhD, CPA, is the KPMG Peat Marwick Professor
of Accounting and René Sacasas, JD, an associate professor
of business law, both at the University of Miami. Elaine Garcia, MPA,
CPA, is with Coopers & Lybrand L.L.P. Ms. Garcia was a graduate
student at the University of Miami when this article was written. On June 30, 1995, AcSEC issued for public comment a proposed Statement
of Position entitled Environmental Remediation Liabilities. If approved
by AcSEC and cleared for issuance by the FASB, the SOP would constitute
the most authoritative guidance available on the accounting for environmental
liabilities. The guidance generally would apply where remediation is required
because of the threat of litigation, a claim, or an assessment. The exposure
draft includes two primary parts. Part I provides an overview of environmental
laws and regulations. Part II addresses the accounting issues. Additionally,
included in the appendices are the current authoritative guidance (appendix
A), a remediation liability case study (appendix B), and audit considerations
(appendix C). The primary accounting provisions proposed can be summarized as follows:
Overall Approach * Based on probable and reasonably estimable criteria of SFAS No. 5,
Accounting for Contingencies. Benchmarks for Accrual/Evaluation of Estimated Liability * Identification and verification of an entity as a potentially responsible
party (PRP) * Receipt of unilateral administrative order * Participation, as a PRP, in the remedial investigation/feasibility
study (RI/FS) * Completion of feasibility study * Issuance of Record of Decision (ROD) * Remedial design through operation and maintenance, including postremediation
monitoring Amount of Liability--Overall Approach * Entity's allocable share of liability for a specific site * Entity's share of amounts related to the site that will not be paid
by other PRPs or the government Costs Included in Liability * Incremental direct costs of the remediation effort * Costs of compensation and benefits for employees to the extent an
employee is expected to devote time directly to the remediation effort
Examples of Incremental Direct Costs * Fees to outside law firms for work related to the remediation effort
* Costs related to completing the RI/FS * Fees to outside engineering and consulting firms for site investigations
and development of remedial action plans and remedial designs * Costs of contractors performing remedial actions * Government oversight costs and past costs * Cost of machinery and equipment dedicated to the remedial actions
that do not have an alternative use * Assessments by a PRP group covering costs incurred by the group in
dealing with a site * Costs of operation and maintenance of the remedial action, including
costs of postremediation monitoring required by the remedial action plan
Effective Date and Transition * Years beginning after December 15, 1995 * Treated as change in accounting estimate--current and prospective
treatment; retroactive adjustment prohibited * JANUARY 1996 / THE CPA JOURNAL
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