1991-053
Use of TAPS construction camp pads by YPC
Cite as Alaska Op. Att'y Gen. No. 1991-053
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department
of Natural Resources
663-91-0531
465-3600
Use of TAPS construction
camp pads by YPC
Robert K. Reges Jr.
Assistant Attorney General
Natural Resources Section - Juneau
The Yukon Pacific Corporation (YPC) proposes to construct
a liquified natural gas (LNG) pipeline from the North Slope to
Valdez.
Because YPC's pipeline would roughly parallel the route
taken by the Trans Alaska Pipeline System (TAPS) oil line, YPC
could utilize certain construction camp pads built by Alyeska for
TAPS.
This would have the environmental benefit of confining
ecosystem-disturbing activities to a limited area.
Accordingly,
Alaska's Department of Natural Resources (DNR) -- manager of the
pads and surrounding lands -- favors reuse of existing pads.
YPC
is concerned, however, that its use of these pads will render it
liable for environmental degradation occasioned by previous users.
Given this dilemma, your department sought our opinion on three
questions related to YPC's proposed use of TAPS pads.
1.
Who is liable for camp pad cleanup if the pads are
contaminated?
2.
Is an environmental audit required at each site?
If
so, who pays for it?
3.
What is YPC's liability if they reuse one of these
sites without first conducting an environmental
audit?
In brief, the answers are these:
Alyeska and the State
of Alaska are liable for any currently existing contamination.
YPC
is not.
An environmental audit is a practical necessity but not a
legal requirement.
Who pays for an audit is a matter totally open
to negotiation.
If YPC reuses the camps without an audit or other
precautionary measure it will become jointly, severally, and
strictly liable for all contamination unless it proves, by a
preponderance of the evidence, that its contribution to the problem
is divisible.
ANALYSIS
I.
WHO IS LIABLE?
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department of Natural Resources
Our file #663-91-0531
Page 2
Strict liability for the release of hazardous substances
is established in state law by AS 46.03.822 and in federal law by
the
Comprehensive
Environmental
Response,
Compensation
and
Liability Act (CERCLA). 1/
Persons made liable by Alaska's law can
be categorized as:
1.
Hazardous substance owner/operator:
the person(s)
who owned or controlled the substance at the time it was
released into the environment;
2.
Present site owner/operator:
the person(s) having
a propriety interest in, or operational control over, the
contaminated site at the time response actions are
commenced;
3.
Past
owner/operator:
the
person(s)
having
a
propriety interest in, or operational control over, the
site at the time hazardous substances were disposed on-
site;
4.
Arranger:
the person(s) who arranged for disposal
of the hazardous substance;
5.
Transporter:
the person(s) who transported the
hazardous substance to the site if the site was selected
by that person. 1/
These
persons
are
generically
called
potentially
responsible
parties (PRP).
CERCLA's reach is probably as broad as AS 46.03.822, but
the federal law does not expressly extend liability to hazardous
substance owners (category 1 above).
See 42 U.S.C.S. 9607(a)
(1989).
However, the person who generated the substance, the
person who owned the substance, and the person who arranged for its
disposal are usually one entity.
This circumstance allows federal
law
to
reach
substance
owners
under
"arranger"
liability.
1/
42 U.S.C. 9601 et seq.
Other federal laws may be applicable,
depending upon the nature of contamination (i.e., Toxic Substances
Control
Act
regulates
activities
involving
Polychlorinated
biphenyls (PCBs)).
For purposes of this memorandum we will assume
that CERCLA would be the primary federal law while other federal
laws would be treated under CERCLA as applicable, relevant, and
appropriate requirements (ARARs).
2/
AS 46.03.822(a)
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department of Natural Resources
Our file #663-91-0531
Page 3
Furthermore, courts broadly construe the PRP categories.
For
instance, in U.S. v. Aceto Agricultural Chem. Corp., 872 F.2d 1373
(8th Cir. 1989), companies that supplied technical grade pesticides
to a formulator for mixing were held liable as "arrangers for
disposal" when the formulator spilled his pesticide product.
Accordingly, it is reasonable to assume that liability under
federal law is coextensive with liability under state law.
The parties of significance to this case are YPC, the
State of Alaska, and Alyeska.
Alaska owns the subject realty,
Alyeska is the past and present operator and YPC is a prospective
operator/lessee who has not yet acquired any interest in, nor
conducted
any
activity
on,
the
pads.
1/
If
the
pads
are
contaminated
at
this
time,
Alyeska
and
the
state
are
both
potentially responsible.
YPC is not.
Alyeska is potentially liable as a past and present
operator.
Int'l Clinical Laboratories, Inc. v. Stevens, 1990 WL
43971, 20 Envtl. L. Rptr. 20560 (E.D.N.Y. 1990) (lessee may be
liable as an operator).
Alaska is potentially liable as a past and
present owner.
Pennsylvania v. Union Gas Co., 491 U.S. 1, 109 S.
Ct. 2273, 105 L. Ed. 2d 1 (1989) (States may be liable as PRPs
under CERCLA if they own a contaminated site). 1/
YPC does not fit
3/
Information provided by your department informs us that YPC is
not connected, in any way, to operations previously conducted on
the sites, to substances used there, or to entities that used those
substances.
This memorandum is founded on those premises.
4/
There is no question that states may be liable under CERCLA.
That law imposes liability on "any person" who falls into the
described categories of PRP.
42 U.S.C.S. 9607(a) (1989).
And,
it defines "person" to include states.
42 U.S.C.S 9601(21)
(1989).
Alaska law, on the other hand, is not so unequivocal.
It
levies liability upon "persons", AS 46.03.822(a), but fails to
define that term.
AS 46.03.826.
However, Alaska's law exempts
"the state or a municipality" from liability under certain special
circumstances.
AS 46.03.822(c)(2),(5); (h).
Such exemptions would
be meaningless unless states were otherwise liable.
Legislators
are presumed to act meaningfully.
Isakson v. Rickey, 550 P.2d 359,
364 (Alaska 1976).
Therefore, Alaska may expect to be held liable
under state law if these pads prove to be contaminated.
The fact that the problem was caused by a lessee is no
defense.
United States v. R.W. Meyer, Inc., 889 F.2d 1497, 1507
(6th Cir. 1991).
Of course the state ultimately has a right of
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department of Natural Resources
Our file #663-91-0531
Page 4
into any of the PRP categories.
Thus, Alaska and Alyeska are
potentially
jointly
and
severally liable for cleanup of any
contamination now existing on the camp pads.
U.S. v. Chem-Dyne
Corp., 572 F. Supp. 802 (S.D. Ohio 1983) (liability under CERCLA is
joint and several). 1/
If YPC elects to use the sites it must lease them from
the state.
YPC will then confront liability as both an "owner" and
an operator.
BCW Associates, Ltd. v. Occidental Chemical Corp.,
1988 WL 102641 (E.D. Pa. 1988) (lessees may be liable as "owners").
Unless certain prophylactic measures are taken (as discussed
below), that liability would extend to pre-existing conditions as
well as contamination YPC might create.
II.
IS AN AUDIT REQUIRED?
As was discussed in an opinion issued earlier this year
(1991
Inf.
Op.
Att'y
Gen.
(Mar.
22;
665-91-0115)),
phased
environmental audits have become a commonplace technique for
characterizing environmental conditions extant on a particular
parcel at a particular time.
Typically, an audit is conducted in
phases.
A Phase I audit is a basic screen for the possible
existence of hazardous substances on the site.
It includes a
visual inspection of the parcel and a review of records associated
with the property.
A Phase II audit involves field sampling.
indemnification by its lessee, Alyeska.
Right-of-Way Lease for the
Trans-Alaska Pipeline Between the State of Alaska and Amerada Hess
Corp., ARCO Pipe Line Co., Exxon Pipeline Co., Mobil Alaska
Pipeline Co., Phillip Petroleum Co., Sohio Pipe Line Co., and Union
Alaska Pipeline Co. 10, 13, 14, 18, 22 and Stipulation thereto
2.2, 2.12, 3.9.
However, such right does not protect the state
from liability to the United States or third parties.
Mardan
Corp. v. C.G.C. Music, Ltd., 804 F.2d 1454, 1459 (9th Cir. 1986).
5/
The Chem-Dyne holding was expressly endorsed by the U.S.
Congress in H.R. Rep. No. 99-253(I), 99th Cong., 1st Sess. 74
(1986).
Joint and several liability is expressly made the standard
in state law.
AS 46.03.822(i).
Other parties, particularly subcontractors of Alyeska, may be
liable.
Because some of the pads were owned by the federal
government, the United States may also be liable.
FMC Corp. v.
U.S. Dep't of Commerce, 1990 WL 102941, 20 Envtl L. Rptr 21403
(E.D. Pa. 1990), not reported in F. Supp., (federal government may
be liable under CERCLA).
However, the record is devoid of any
facts specifically pointing to other PRP's, so this memorandum does
not concern itself with them.
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department of Natural Resources
Our file #663-91-0531
Page 5
It makes little sense to conduct a Phase I audit in this
case
because
all
concerned
parties
know
that
the
pads
were
previously
used
for
industrial
practices
involving
hazardous
materials
(paints,
petroleum
products,
various
metals,
miscellaneous hydrocarbons, etc.).
The only purpose served by
reviewing records of past activities would be to circumscribe the
universe
of
contaminants
likely
to
be
encountered.
Such
circumscription might facilitate design of sampling plans and
thereby expedite Phase II sampling.
Field sampling (borings, surface water samples, ground
penetrating radar, soil vapor surveys, etc.) would be a logical
endeavor.
Unlike some states, Alaska law does not mandate testing
before transacting property interests. 1/
However, we know of no
other
means
for
assessing
environmental
conditions,
and
an
assessment of conditions is requisite to any rational allocation of
responsibility among the PRPs. 1/
Thus, auditing environmental
conditions is prudent.
III.
WHO PAYS FOR THE AUDIT?
This is a matter of negotiation.
While this office will
not speculate on the strengths and weaknesses of the state's
bargaining position, there is one matter that must be addressed at
this juncture because it must be understood in order to appreciate
what is negotiable and what is not.
That is the matter of
"innocent land owner" status.
In correspondence to YPC, your
department suggested that an environmental audit might allow YPC to
"escape liability as an innocent third party."
Because it would be
extremely difficult for YPC to qualify for this status -- commonly
called
"innocent
land
owner"
--
YPC
cannot
be
expected
to
contribute funds in the hope of securing such status.
6/
Compare, for instance, New Jersey's Environmental Cleanup
Responsibility Act (ECRA), NJSA 13:1K-6 et seq., which requires
owners or operators of "industrial establishments" to assess
environmental conditions and clean any existing environmental
problems before closing or transferring title to the establishment.
7/
Of
course,
Alyeska
and
YPC
could
arbitrarily
divvy
up
responsibility between themselves without knowing the actual scope
of that responsibility.
The cost of an audit would be saved, but
one party risks accepting more than its fair share of liability.
Moreover,
the
state
could
not
engage
in
such
an
arbitrary
allocation.
While a private entity may choose to accept unlimited
risks, the state cannot afford to be so cavalier with public funds.
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department of Natural Resources
Our file #663-91-0531
Page 6
"Innocent
land
owner"
status
is
bestowed
by
AS 46.03.822(b)(1)(B) and 42 U.S.C. 9607(b)(3).
Reduced to its
essence, the law holds that any person otherwise liable for a
release or threatened release of hazardous substances can avoid
liability if that person proves --
by a preponderance of the
evidence 1/ -- that the release is solely attributable to a third-
party not in privity with the person and that the release occurred
despite that person's due diligence and best efforts to avoid or
remedy the release.
Assuming
that
YPC leases the pads from Alaska, or
subleases them from Alyeska, YPC will thereafter be in privity with
responsible third parties.
That will prevent YPC from acquiring
innocent land owner status as to future releases.
AS 46.03.822(c).
However, because YPC is not now in privity with Alyeska or Alaska
as to these pads, the element of privity does not bar YPC from now
acquiring innocent land owner status for past releases.
The aforementioned elements of due diligence and best
remedial efforts do frustrate YPC's chances of achieving "innocent
land owner" status as to past releases.
To satisfy due diligence
requirements, YPC would have to conduct a thorough Phase II
sampling of the pads.
This is necessary (despite the lack of a
legal mandate to do so) because past uses of the site and readily
ascertainable information make the likelihood of contamination
obvious.
AS 46.03.822(d).
Add to that YPC's specialized knowledge
as a sophisticated investment company and it becomes clear that the
diligence due includes field sampling.
See AS 46.03.822(d).
And,
if sampling reveals contamination, best remedial efforts require
on-the-ground corrective action.
AS 46.03.822(b)(2)(B).
Thus,
"innocent land owner" status is achievable only upon considerable
expense.
Consequently, attainment of innocent land owner status is
not likely to motivate YPC into financing environmental audits.
Nonetheless Alaska, Alyeska, and YPC can be expected to
share the cost of audits.
Alaska and Alyeska have motivation to
contribute because they are already jointly and severally liable
for the complete costs of assessment and cleanup at the sites.
AS 46.03.822(a); O'Neil v. Picillo, 883 F.2d 176 (1st Cir. 1989),
8/
The "preponderance" standard is expressly established in
federal law.
42 U.S.C.S 9607(b)(3) (1989).
Although Alaska's
law simply says that the defense must be proved -- and fails to set
a standard of proof --
it is well accepted that affirmative
defenses must be proved by a preponderance of the evidence.
Clucas
v. State, Op. No. 1147 (Alaska App. July 19, 1991); 1991 WL 132019.
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department of Natural Resources
Our file #663-91-0531
Page 7
cert. denied, 110 S. Ct. 1115 (1990) (liability under CERCLA is
strict, joint, and several).
In other words, either Alaska or
Alyeska could be forced -- by the Environmental Protection Agency
or a third person -- to bear the entire cost of an environmental
assessment. 1/
YPC has motivation to contribute some portion of
the savings it would realize by not having to construct new sites.
Accordingly,
the
cost
of
an
audit
would
be
allocated
by
negotiation.
IV.
WHAT IS YPC's LIABILITY IF NO AUDIT IS CONDUCTED?
Absent an audit, no one will know whether the pads are
contaminated.
At some time, sooner or later, their condition is
likely to be assessed. 1/
If the pads are ultimately found to be
clean, no liability arises.
If, following YPC's use, the pads turn
out to be contaminated, YPC will be liable for all existing
contamination unless it can prove that damages are divisible among
the PRPs.
AS 46.03.822(i); O'Neil, 883 F.2d at 178 (damages should
be apportioned only if a defendant can demonstrate that the harm is
divisible).
Such proof would be extremely difficult to make in the
absence of an audit, since baseline conditions would not be known.
YPC could limit its liability up-front by purchasing -
from Alaska, Alyeska, and the U.S.-EPA -- covenants not to sue.
Nothing in present state or federal law prevents one private party
from agreeing not to sue another private party. 1/
An agreement
between Alyeska and YPC should be achievable.
9/
EPA's
authority
to
force
assessment
can
be
found
in
42 U.S.C.S. 9606, 9607 (1989).
Third-parties may sue under
various federal citizen suit provisions.
E.g., 42 U.S.C.S. 9659
(1989); 42 U.S.C.S. 6972 (1989).
10/
As pointed out in the informal opinion of March 22, 1991 (1991
Inf. Op. Att'y Gen. (Mar. 22; 665-91-0115)), audits are now so
commonplace that DNR must assume that the environmental condition
of these pads will eventually be assessed.
11/
In fact, the right of private parties to buy and sell risks is
expressly preserved.
AS 46.03.822(g); 42 U.S.C.S. 9607(e)(1)
(1989).
Niecko v. Emro Mktg Co., ____ F. Supp. ____, 1991 WL
126378, (D.C.E. Mich. Jul. 2, 1991).
While such a covenant may not
limit the legal liability of Alyeska, AM Int'l, Inc. v. Int'l
Forging Equip., 743 F. Supp. 525 (N.D. Ohio 1990) (tortfeasors may
not contract away liability) but see Jones-Hamilton Co. v. Kop-
Coat, Inc., 750 F. Supp. 1022 (N.D. Cal. 1990) (AM Int'l is not the
rule in the Ninth Circuit), it would limit the actual liability
because sale of the covenant would provide Alyeska with monies to
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department of Natural Resources
Our file #663-91-0531
Page 8
No agreement between private persons can be used to
prejudice governmental rights of enforcement or cost-recovery.
Jones-Hamilton Co. v. Kop-Coat, Inc., 750 F. Supp. 1022 (N.D. Cal.
1990).
Consequently, YPC would also have to purchase a covenant
not to sue from Alaska and, if possible, the United States.
Alaska
has inherent power to waive enforcement authority.
1991 Inf. Op.
Att'y Gen. (Mar. 22; 665-91-0115); 1984 Inf. Op. Att'y Gen. (Sept.
28; 366-069-85). 1/
Nothing in Alaska's environmental laws negates
this inherent sovereign power. 1/
Thus, it would appear possible
for the state to issue such a covenant to YPC.
EPA has grappled with this mechanism. 1/
In a guidance
document
1/
"premised
on
the
Agency's
inherent
settlement
authority", EPA stated: "[E]ntering into a covenant not to sue with
a prospective purchaser of contaminated property, given appropriate
environmental safeguards, may result in an environmental benefit
through a payment to be applied to clean-up of the site or a
commitment to perform response action." 1/
EPA then went on to set
minimal criteria for a federally issued covenant not to sue.
First, EPA will not become involved in purely private
commercial
transactions.
Unless
EPA
is
otherwise
pay for partial clean-up.
12/
The case of U.S. v. Bell Petroleum Services, Inc., 21 Envtl.
L. Rptr. 20374 (W.D. Tex. 1990) held that governments have inherent
authority to settle cost recovery claims.
There is no reason to
suppose that such authority arises only upon expenditure.
Thus, a
government would have inherent authority to settle cleanup claims
before costs are incurred.
13/
Although AS 46.08.070(b) requires efforts to recover monies
expended, it does not thwart efforts to avoid those expenditures in
the first instance.
14/
In fact, EPA recently sold a covenant not to sue to a bank
that wanted to foreclose on contaminated land.
22 Envtl. Rptr.
(BNA) Curr. Dvlpmts. 126 (May 17, 1991).
15/
"Guidance on Landowner Liability under Section 107(a)(1) of
CERCLA, De Minimis Settlements under Section 122(g)(1)(B) of
CERCLA, and Settlements with Prospective Purchasers of Contaminated
Property", OSWER 9835.9 (Jun. 6, 1989).
16/
Id. at 27.
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department of Natural Resources
Our file #663-91-0531
Page 9
involved with the property under consideration, it will
not issue a covenant.
Second, in exchange for the covenant EPA must receive
substantial
benefit
not
otherwise
available.
Such
benefit might be monetary, might be a cleanup, or might
be ephemeral, such as retention of scarce employment
opportunities.1/
Third, continued use of the site must not aggravate the
spread of contamination.
Fourth, persons who will work
at the site -- if the covenant issues -- must not be
exposed
to
unreasonable
health
risks.
Fifth,
the
recipient of the covenant must demonstrate that it is
financially capable of fulfilling any obligations it
takes on in exchange for the covenant.
EPA's guidance goes on to discuss possible forms the
covenant might take.
Drafting a covenant should also be guided by
CERCLA 1/, by EPA's model 1/ and by previously issued covenants. 1/
17/
Avoiding massive lay-offs was a primary goal of Michigan and
the U.S.-EPA when they issued a covenant not to sue to LOMAC, Inc.
for the BOFORS site in Muskegon, Michagan.
See, Obtaining a
Covenant Not to Sue from the Government -- The Acquisition of a
Contaminated Site by an Innocent Purchaser: The BOFORS, Michigan
Site, A New Beginning After SARA, Stewart H. Freeman and Stanley F.
Pruss (Apr. 20, 1987), printed in Hazardous Waste Litigation after
the RCRA and CERCLA Amendments of 1987, Practising Law Institute
(Jun. 1987).
18/
CERCLA expressly provides for the issuance of covenants not to
sue in certain cases.
42 U.S.C.S. 9622(f) (1989).
The law lists
factors to be considered when deciding whether to issue a covenant
and
how
broad
to
make
any
such
covenant.
42
U.S.C.S.
9622(f)(4-6) (1989).
Because that provision only applies when
issuing a covenant to a person who is already a PRP, U.S. v. Bell
Petroleum Services, Inc., 21 Envtl. L. Rptr. 20374, it is not
binding in the case of YPC.
However, the law provides a useful
guide.
19/
On July 10, 1987, EPA issued guidance entitled "Covenants Not
to Sue Under SARA."
Memorandum from Thomas L. Adams, J. Winston
Porter and F. Henry Habicht to Regional Administrators.
Included
in that guidance was a model covenant.
20/
The documents prepared for the BOFORS site are reproduced in
the referenced text. See n. 15.
The Hon. Harold C. Heinze
September 5, 1991
Commissioner, Department of Natural Resources
Our file #663-91-0531
Page 10
This office can assist you with negotiations and drafting should
you elect to pursue this route.
V.
CONCLUSION
Yukon Pacific Corporation will save construction costs if
it employs pre-existing camp pads.
Alaska's Department of Natural
Resources -- manager of the state-owned pads -- encourages such
reuse of impacted areas.
Not only will such reuse concentrate
environmental impacts, it will bring in money that can be used to
offset
the
state's
present
liability
for
any
existing
contamination.
However, DNR (and DEC) wish to ensure that all
foreseeable environmental impacts have been considered before any
permit or lease agreement is executed.
To achieve such assurances,
a Phase II environmental audit should be conducted at each site,
costs to be shared by Alaska, Alyeska, and YPC according to the
pro-rata benefits to be gained by each.
As for sites found to be
contaminated, DNR might sell YPC a covenant not to sue in exchange
for contribution toward clean-up costs.
RKR:lmk