# Petition for Writ of Certiorari — Campbell v. California

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## Record

- **Collection:** Supreme Court brief
- **Document type:** Petition for Writ of Certiorari
- **Published:** January 1, 1998
- **Citation:** 525 U.S. 822

## Text

Supreme Court, us
FILED

S71996 UUs 199

OFFICE OF THE Crea.
In The

Supreme Court of The United States
October Term 1997

N°.

+

ALBERT CAMPBELL, et al.
Petitioners,
Vv.

STATE OF CALIFORNIA.
Respondent.

4
Petition For A Writ Of Certiorari_
To The United States Court of
Appeals For The Ninth Circuit
4

PETITION FOR WRIT OF CERTIORARI

¢

LOUISE BURDA GILBERT*

DALE C. CAMPBELL
Weintraub, Genshlea & Sproul
400 Capitol Mall, 11th Floor
Sacramento, California 95814
(916) 558-6000

Attorneys for Petitioners
*Counsel of Record

AERTS UIT

APPELLATE ADVANTAGE
4264 N. OAK TRAFFICWAY@KANSAS CITY, MO 641164816-453-2424

QUESTION PRESENTED FOR REVIEW

The question presented by this petition for writ of
certiorarl 1s Whether a mandatory permanent injunction
compelling the expensive remediation of off-site
contamination under a complaint brought under CERCLA can
be based upon summary judgment on a pendant state law
public nuisance claim where the determination of causation

of the off-site contamination is disputed and where the

defendants have not been afforded any discovery.

LIST OF PARTIES TO THE PROCEEDINGS
IN THE COURT BELOW

Appellants:

Albert Campbell and Charles Tackman, as the Executors of
the Estate of Victor Muscat

Appellants Attorneys: L. Burda Gilbert
Dale C. Campbell |
Weintraub Genshlea & Sproul
Law Corporation
400 Capitol Mall, 11th Flr.
Sacramento, CA 95814

Appellee: |
State of California

Appellees Attorney: Sandra Goldberg
Attorney General’s Office of
the State of California
Deputy Attorney General
2101 Webster St., 12th Flr.
Oakland, CA 94612-3049

i

TABLE OF CONTENTS

Page
(uention Presented fOr REVIEW . 0. ees
List of Parties to the Proceedings ........ 2.20650 5s 1
ERAS Ns ne Reena ms ances er Pg a ae il]
I a RRO iy egw hw Wo aN 1\
6 Sa ae = Oe bee Pe err eee Pe ee
a ee ee a ts va mw telalw arena ese 2 :
eaiemae Saver ver tr) tis CASE 6 es oe is ee eee os 3
NE HE ey eS Ded yea ew ie ko 7
Reasons for Granting the Writ... 6.0.66 8 een. 7
II de to te aes gS a ka wee 22
Appendices
RE Ceska sae cka seh be ieia cde. A-|]
UI, Tesh eo es ee a cea bone B - 5]
PR ek a key Ke ern C-128

il

TABLE OF AUTHORITIES

CASES
Page

Bellflower v. Pennise,

SAG F270 770 (ie CARs TPT T) ee ea eer en 18
Bradley v. Armstrong Rubber Co..,

(36s 5a toe Ce A CE? kta eee 19
Carter v. Chotiner,

SI ERE G6 UI IOO) ii oa ieee eee ee 13
Johnson v. Hospital Corp. of America,

OS F.3d. 563: (500 Cit. P96) 8 iy oo
McGregor vy. Industrial Excess Landfill, Inc.,

709 F.Supp 1401 (N.D. Ohio 1987)

aff'd, 856 F.2d 39 (6th Cir. 1988) ............. 20
State of California v. Campbell,

L356 FSG 772 Fm Ch. VIB) oe es big hd, &3
Taylor Bay Protective Assoc. v. ADM'R, U.S. E.P.A.,

BSE P20 107 5 OG. Toe iss ee ee ee 17

Town of Orangetown vy. Gorsuch,

718 F.2d 29 (2nd Cir. 1983) |7

Sterling v. Velsicol Chemical Corp

855 F.2d 1188 (6th Cir. 1983) a ae ee
U.S. v. Cannon Engineering Corp.,
720 F.Supp. 1027 (D. Mass. 1989)

affd S99:F 26.79. tit Cit. {POO} i a ea ae

U.S. v. Conservation Chemical Co.,

619 F.Supp 162 (D.C. Mo. 1985) Chass ee

CONSTITUTIONAL AND STATUTORY PROVISIONS

Chapter 103, Subchapter |, Section 106
of the Comprehensive Environmental

Response, Compensation and Liability Act

(CERCLA) 42 U.S.C. § 9606(a) , ae Soe
28 U.S.C.§ 1254 (1993) .. 3
California Civil Code § 3479 ....... fe en a ae
California Civil Code § 3480 ..... Cites eer Sian

MISCELLANEOUS

66 C.J.S. Nuisances § 8(b) (1950)

18
S8 Am. Jur 2p, Nuisance § 24 (1989 1S
RULES
Supreme Court Rule 13.1

PETITION FOR WRIT OF CERTIORARI
lhe executors of the Victor Muscat estate respectfully
pray that a writ of certiorari issue to review the judgment and
opinion of the United States Court of Appeals for the Ninth
Circuit entered in this proceeding on March 9, 1998, in order

to resolve the important issue presented herein

OPINIONS BELOW
The opinion of the United States Court of Appeals for
the Ninth Circuit that gives rise to this petition is published.
It is reprinted in Appendix A ("Apdx. A") hereto
[he opinion of the United States District Court for the
Eastern District of California which gave rise to the appeal to

the Ninth Circuit is unpublished. It 1s reprinted in

\ppendix B ("Apdx. B") hereto

STATEMENT OF JURISDICTION

On August 5, 1993, the United States District Court
for the Eastern District of California issued an order granting
summary judgment to plaintiff, the State of California ("the
State"), on its state law claim for public nuisance, in effect
finding that a public nuisance had been "maintained" by
appellants, the executors of the estate of Victor Muscat.
during the instant of time that certain real property held by the
decedent passed through his estate Into a testamentary trust.
In that same order, the District Court granted a mandatory
permanent injunction which incorporated an administrative
order previously issued by the State which, among other
things, ordered the executor appellants to remediate alleged
off-site contamination at the Stanley Park subdivision which

is located approximately one mile away from the estate

property.

On September 7, 1993, defendants filed a notice of
appeal to the United States Court of Appeals for the Ninth
Circuit. The Ninth Circuit affirmed the District Court in an
opinion filed on March 9, 1998. Pursuant to Supreme Court
Rule 13.1, this petition has been filed within 90 days of the
opinion of the Ninth Circuit. This Court has jurisdiction

under 28 U.S.C. section 1254 (1993),

STATUTES INVOLVED IN THIS CASE
Chapter 103, Subchapter I, Section 106, of the
Comprehensive Environmental Response, Compensation and
Liability Act (CERCLA), 42 U.S.C. section 9606(a) (1980)
provides in part:

In addition to any other action taken by a State

or local government, when the President
determines that there may be an imminent and
substantial endangerment to the public health

or welfare or the environment because of an

actual or threatened retease of a hazardous

+
5

substance from a facility, he may require the
Attorney General of the United States to
secure such relief as may be necessary to abate
such danger or threat, and the district court of
the United States in the district in which the
threat occurs shall have jurisdiction to grant
such relief as the public interest and the
equities of the case may require. The
President may also, after notice to the affected
State, take other action under this section
including, but not limited to, issuing such
orders as may be necessary to protect public

health and welfare and the environment.

Cah fornia Civil Code section 3479 provides:

Anything which is injurious to_ health,
including, but not limited to, the illegal sale of
controlled substances, or 1s indecent or
offensive to the senses, or an obstruction to
the free use of property, so as to interfere with
the comfortable enjoyment of life or property,
or unlawfully obstructs the free passage or
use, in the customary manner, of any
navigable lake, or river, bay, stream, canal, or
basin, or any public park, square, street, or

highway, Is a nuisance.

California Civil Code section 3480 provides

A public nuisance is one which affects at the
same time an_ entire community or
neighborhood, or any considerable number of
persons, although the extent of the annoyance
or damage inflicted upon individuals may be

unequal.

STATEMENT OF THE CASE
This is a CERCLA action combined with a pendant
public nuisance claim under state law. The State of California
(the "State”), within only 70 days of the filing of the
complaint, and without any discovery by any party, sought

;

and obtained summary adjudication for a mandatory

permanent injunction on its pendant state law public nuisance
claim. The injunction ordered appellants to comply with a

comprehensive administrative order pre\ iously issued by the

State which required appellants as executors of an estate,

‘sat

among other things, to construct a major water line to a
distant subdivision to remedy the impact of groundwater
contamination at the subdivision located over one mile away
from the property briefly administrated by appellants.

In opposition to the State’s motion, appellants offered
facts and expert opinion indicating that the off-site
contamination at the subdivision was not caused by
contamination from the property administrated by appellants
but rather was caused by contamination created at another
industrial facility, Louisiana Pacific, located midway between
the property administrated by appellants and the subdivision.

The District Court denied appellants any discovery,
denied their request for a continuance, found liability on the
public nuisance claim and issued the comprehensive
mandatory permanent injunction.

The Ninth Circuit affirmed. In doing so, the Ninth

Circuit held inconsistently that the facts and evidence sought

ind Otfered D appellants which would establish anothet
cause of the contamination off-site al Me subdivision, the

Louisiana Pacific Property, were “immaterial to the state law

Louisiana Pacific Property, “mandated” a conclusion that the
property administrated by appellants was the cause ol

contamination at the subdivision

REASONS FOR GRANTING THE WRIT

nderilving action is in federal court because It Is

ye? iT
a CERCLA case brought by the State of California which
seeks cost recovery and other relief related to soil and
vroundwater contamination caused by the alleged imprope!

disposal of trichloroethylene ("TCE") at a manufacturing

facility known as Victor Industries. The State of California

(the "State") appended onto its federal CERCLA complaint a

state law tort claim fer public nuisance by which the State
sought injunctive relief. Prior to filing the complaint, the
State had issued an administrative order directing appellants
not only to remediate the soil and groundwater contamination
at Victor Industries, but also to remediate TCE contaminated
groundwater beneath a residential development known as
Stanley Park, located more than one mile away from Victor
Industries.

Only 70 days after filing the complaint and before
appellants had filed an answer or conducted any discovery,
the State filed a motion for summary adjudication on the state
law tort claim of public nuisance asking the District Court to
adopt verbatim the previously issued administrative order as
a mandatory permanent injunction. The State’s motion for

summary adjudication also requested a finding that

appellant's were liable as Responsible Parties under

CERCLA, but did not request judgment imposing a CERCLA
injunction or for a cost recovery determination.

Due to the short period of time between the filing of
the complaint and the motion for summary judgment,
defendants were unable to take any discovery and were forced
to defend the comprehensive summary judgment motion
based only upon limited existing information available from
public sources and the opinion of their expert, Jay Lucas.
Mr. Lucas had previously been employed by the California
Department of Health Services, Toxic Substances Control]
Division (predecessor to the Department of Toxic Substances
Control) and was at the time of the motion employed with
Brown & Caldwell Consultants who were investigating the
Victor Industries site for the Victor Muscat Trust
Significantly, Mr. Lucas had not done any off-site

investigation and could rely only upon incomplete data and

test results and reports in the public record.

Notwithstanding the limited time and the appellants’
inability to conduct any discovery whatsoever in the action,
appellants submitted credible and persuasive expert testimony
and opinion opposing the State’s motion for summary
adjudication. Appellants’ expert refuted the State’s proffered
facts and opinion that the contamination at Victor Industries
{also known as the 20th Street Property] was the source, and
therefore the legal cause, of the contamination one mile away
at Stanley Park. (Apdx. C.) Appellants’ expert offered facts
and opined that the likely cause of the contamination at
Stanley Park was another industrial facility, Louisiana Pacific,
which was midpoint between Victor Industries and Stanley
Park. (See Apdx. C, generally, and pages C - 137-8, 151,
157, 161 specifically.) Appellants also moved the District
Court for a continuance to allow an opportunity to gather
additional evidence to further support their expert's opinion.

In response, the State filed rebuttal opinions which challenged

LO

so eeiceeeeniiieaiiitieiieiiaaliaaiaiihiiaiiiaaiiil

challenged the reasonable conclusions and opinions submitted
by appellants’ expert. The State's rebuttal highlighted the fact
that disputed issues of fact existed concerning the source, or
cause, of the contamination at Stanley Park.

The District Court denied the request for a
continuance, granted the State's motion for summary
adjudication, and adopted verbatim the previously issued
administrative order as a mandatory permanent injunction on

the nuisance claim.

Lucas evidence does create a dispute - or, in the words of the
summary adjudication statute, an ‘issue’ - between the parties:
Lucas's evidence suggests that the Louisiana Pacific Property
contaminated the water at Stanley Park "State of

}

California v. Campbell, 138 F..

772, 781 (9th Cir. 1998)

(Apdx. A.) The Ninth Circuit then went on to erroneously

hold that the facts and opinion submitted by appellants’ expert

did not raise genuine issues of material fact because "[t}he
cause of the trichloroethylene contamination at Stanley Park
and other off-site areas is therefore immaterial to California’s
state law claims." State of California v. Campbell, 138 F.3d
772, 781 (9th Cir. 1998). (Apdx. A.) The Ninth Circuit also
reiterated its opinion that causation of the Stanley Park
contamination was immaterial to the nuisance claim when it
upheld the District Court’s denial of appellants’ request for a
continuance to allow additional time to obtain corroborative
evidence that the Stanley Park contamination originated from
the Louisiana Pacific facility:

The undisputed evidence that
trichloroethylene contaminated the soil and
groundwater at the 20th Street Property \s
sufficient to establish the defendants’ liability
under Califorma law. To succeed on its
summary adjudication motion, California need
not prove that property other than the 20th

Street Property suffered from contamination.

Under California law, the pollution at the 20th

Street Property constitutes a public nuisance
and violates California's environmental laws.
See Carter v. Chotiner, 210 Cal. 288, 291,
291 P. 577 (1930) (polluted water 1s a public
nuisance); Cal. Health & Safety Code §
25§358.3 (W hen a release or threatened release
of hazardous substances endangers — the
environment, those responsible may have to
take remedial action). Therefore, any
additional data about contamination at
property other than the 20th Street Property 1s
not relevant to oppose the summary
adjudication motion.

7

State of California v. Campbell, 138 F.3d 772, 781 (9th Cir.
1998). (Apdx. A.) .

The Ninth Circuit then issued a further internally
inconsistent holding by denying appellants’ challenge to the
scope of the injunction. The glaring internal inconsistency 1s

that in order to uphold the broad scope of the injunction

requiring expensive remediation off-site at Stanley Park, the

Ninth Circuit had to contrive a way to reject appellants’

~
4

expert's declaration which the Ninth Circuit had earlier
acknowledged did create a disputed "issue." The Ninth
Circuit accomplished this by finding that "no reasonable juror
could conclude that the Louisiana Pacific Property, rather than
the 20th Street Property [Victor Industries|, was the source of
the contamination at Stanley Park." State of
California v. Campbell, 138 F.3d 772, 781 (9th Cir. 1998).
(Apdx. A.) The basis for this controverted "finding" rests on
the fact that at this very early stage of the litigation, and
without any discovery whatsoever, there were no undisputed
facts presented by appellants to show that Louisiana Pacific
disposed of TCE on its property to support the appellants'
expert’s opinion that Louisiana Pacific was the source of the
contamination at Stanley Park. That evidence, of course. was
the very evidence appellants sought to obtain in moving for a
continuance to conduct discovery, the discovery which the

Ninth Circuit earlier in its opinion held was "immaterial" to

14

the State claims and did not warrant a continuance because
the evidence sought was not calculated to obtain “facts
essential” to resist the summary adjudication. If these facts
are not “essential” to resist summary adjudication, then the
absence of those very facts can not be used to reject the
opinion of an otherwise qualified expert that the
contamination at Stanley Park originated from the Louisiana
Pacific Property.

The error of this reasoning 1s made more obvious by
evidence submitted by the State's own expert which indicated
that contamination had nor occurred on the Victor Industries
Property which evidence corroborated appellants’ expert's
conclusion that the Louisiana Pacific Property was the source
of the contamination in Stanley Park Attached to the
Declaration of Gene Riddle, submitted by the State in support

of its motion, was a report made by Environmental Strategies

Corporation which was prepared for the California

PIS Rn eT ne ee ee

Department of Health Services, Toxic Substances Contro]
Division, Region |, in 1990. In that report. which assesses the
groundwater contamination at the Victor Industries Property,
Environmental Strategies Corporation concludes:

Based on the results of the field
Investigation, ESC concludes that there is no
significant: contamination in the shallow
unconfined groundwater or soils between
depths of 5 feet and 35 feet at the former

Victor Industries 20th Street site

ESC concludes that no further
groundwater contamination should result -
from the infiltration of soil leachate to the

water table

The results of this investigation
contradict. the earlier soil eas survey
performed by WESTON, which showed TCE
and PCE concentrations of up to. several

hundred ppb in the soil vapo: phase

If significant quantities of volatile
organic Compounds were dumped at the site as

alleged by former employees. one would

lo

expect to find relatively high contaminant
levels in the soils or groundwater. Since high
levels were nor detected during ES¢

investigation, several explanations can be

proposed

- j 1 |
A final explanation could be that
SIGAIICANTE Guantilics Of Solvents were not
| / ’ ) rly “)% , ai ‘
dumped at the 20th Street sit (emphasis

added)

Ihe Ninth Circuit's) published opinion holds
essentially that “causation” is not “essential” to impose
mandatory injunction to remedy an off-site public nuisance
[his opinion conflicts with every other opinion which ha
addressed the issue see, @&.2., Lown of Orangetown \
Gorsuch, 718 F.2d 29 (2nd Cir. 1983) (requiring an
unequivocal finding of causation essential to a public

nuisance claim); Javlor Bay Protective Assoc. v. ADM'R. US

Ik P.A., 884 F.2d 1073 (Sth Cir. 1989) ("| T]he maintenance o

the nuisance must be the natural and proximate cause of the
injury. [citations omitted]. Proximate cause is 'a cause which,
in a natural and continuous sequence, produces damage and
without which the damage would not have occurred... "":
Bellflower v. Pennise, 548 F.2d 776 (8th Cir. 1977) (".. . in
order to constitute an actionable nuisance, not only must a
wrongful act of the defendant be shown but also the
maintenance of the nuisance must be the natural and
proximate cause of the injury.") (citing 66 C.J.S. Nuisances §
8(b) (1950)); Johnson v. Hospital Corp. of America, 95 F.3d
383 (5th Cir. 1996) ("Appellants have not produced any
evidence demonstrating a causal link between their alleged
damages and the chemicals at the disposal sites. It is the well-
accepted general rule that a defendant may not be held liable
for the consequences of an alleged nuisance absent a showing
that he had in fact caused the conditions complained of.")

(citing 58 Am. Jur 2p, Nuisance § 24 (1989); Sterling v.

18

Velsicol Chemical Corp., 855 F.2d 1188 (6th Cir. 1988)

(discussing the sufficiency of evidence to prove the requisite
causation between a disposal of toxic chemicals and plaintiff's
injuries); Bradley v. Armstrong Rubber Co., 130 F.3d 1608
(5th Cir. 1997) (summary judgment for defendants discussing
plaintiff's failure to prove causation).

It is elementary that if the off-site contamination at
Stanley Park was caused by a release of contaminants from
the Louisiana Pacific Property, and not by a release at Victor
Industries Property, then appellants have no duty to remediate
the off-site nuisance and indeed, no ability to abate it by
action taken on the Victor Industries Property.

If allowed to stand, the Ninth Circuit’s opinion will
allow these plaintiffs and others nationwide to circumvent the
federal statutory scheme for addressing environmental
contamination by invoking the jurisdiction of the federal court

under CERCLA and then proceeding on pendant state law

19

claims of public nuisance to obtain relief not available to
them under CERCLA.

Congress has specifically declined to provide the
states with a nght to injunctive relief under CERCLA.
Rather, section 9606 of CERCLA expressly authorizes only
the United States to seek injunctive relief to abate an actual or
threatened release of a hazardous substance from a facility.
The legislative history shows that Congress specifically
declined to provide the States with standing to seek injunctive
relief under CERCLA. An early Senate version of CERCLA
empowered either the United States "or the State” to seek
injunctive relief. That was altered through compromise such
that standing was limited to the United States alone.
U.S. v. Cannon Engineering Corp., 720 F.Supp. 1027, 1052
(D. Mass. 1989), affd. 899 F.2d 79 (Ist Cir. 1990);
McGregor vv. Industrial Excess Landfill, _In

709 F.Supp 1401, 1409 (N.D. Ohio 1987). aff'd, 856 F.2d 39

20

(Oth Cir. 1988): and U.S. v. Conservation Chemical ¢
619 F.Supp 162, 231-232 (D.C. Mo. 1985)

More importantly, the Ninth Circuit's published
opinion, if allowed to stand, will permit plaintiffs natlonwide
to seek to obtain onerous and expensive mandatory clean-up
injunctions and to accomplish this without having to establish
the requisite causal connection between the nuisance and the
harm to be remedied. Requiring such a causal connection ts

a principle fundamental to American jurisprudence.

Certiorari 1s appropriate here

CONCLUSION

For the foregoing reasons, the petition for writ of
certiorar! should be granted.

Respectfully submitted,

L. Burda Gilbert

WEINTRAUB GENSHLEA & SPROUL
Law Corporation

400 Capitol Mall, 11th Floor

Sacramento, California 95814

(916) 558-6000

9,

APPENDIX A

UNITED STATES COURT OF APPEALS
FOR THE NINTH CIRCUIT

FOR PUBLICATION
UNITED STATES COURT OF APPEALS
FOR THE NINTH CIRCUIT

STATE OF CALIFORNIA,
on behalf of the California
Department of Toxic
Substances Control,

Plaintiff-Appellee,

\
ALBERT CAMPBELL, No. 93-16754
individually and as Trustee of D.C. No
the Victor Muscat Testamentary CV-93-00604 GEB
Trusts and Executor of the OPINION

Estate of Victor Muscat;

CHARLES TACKMAN.

individually and as Trustee of the

Victor Muscat Testamentary

Trusts and Executor of the Estate of

Victor Muscat,
Defendants-Appellants,

and
WESTERN RESOURCES, INC...
Receiver of the Victor Muscat

Testamentary Trusts,

/ntervening Defendant.

Appeal from the United States District Court

for the Eastern District of California

Apdx A - |

Garland E. Burrell, District Judge. Presiding
Argued and Submitted
December 9, 1997--Pasadena, California
Filed March 9, 1998
Before: James R. Browning, Harry Pregerson, and

Michael Daly Hawkins, Circuit Judges,

Apdx A - 2

Opinion by Judge Harry Pregerson

SUMMARY

Civil Litigation and Procedure/Appeals-Jurisdiction

The court of appeals dismissed an appeal in part. The
court held that a defendant may appeal from an order granting
summary adjudication to the detendant on state nuisance and
environmental claims when it is part of an order granting. an
injunction

For almost 20 years, workers at Victor Industries, a
manufacturer of metal products in Chico, California, used
trichloroethylene, a carcinogen, as a solvent and disposed ot
it by dumping it on the ground. The California Department of
Toxic Substances tested soil and groundwater and found that
trichloroethylene had contaminated the groundwater and
municipal and private wells located downgradient from
Victor's property. Appellee State of California filed a federal

action to require appellants executors of the estate of Victor
{

\pdx Re. 5

Muscat, Victor's owners and the receiver appointed for his
trust assets, to clean up the contamination and to recover the
money that the State spent investigating the contamination.

The district court granted California's motion for
summary adjudication of its claims under the Comprehensive
Environmental Response, Compensation, and Liability Act
(CERCLA) and state nuisance and environmental laws. As a
remedy for the violations of California law, the court issued an
injunction that required defendants to abate the nuisance
caused by the contamination. The trustees appealed.

[1JAs a general rule, federal courts of appeals have
jurisdiction only over final decisions of the district courts. A
final decision is one that ends the litigation on the merits and
leaves nothing for the court to do but to execute the judgment.
An order that determines liability but not damages is not a
final decision, nor is an order that adjudicates less than all

claims.

Apdx A -4

[2] The district court's CERCLA order determined that
the defendants were liable for California's investigation costs
but did not determine what those costs were. The state-law
order resolved the nuisance and environmental claims, but left
other claims unresolved. Unless the summary adjudication
orders fell under an exception to the final judgment rule, the
court of appeals had no jurisdiction to hear them

[3]The small category of decisions that may be
considered "final" even though they do not end the litigation
includes only decisions that are conclusive, that resolve
important questions separate from the merits, and that are
effectively unreviewable on appeal from the final judgment in
the underlying action. [4] The district court's summary
adjudication orders were not among this small category of
appealable collateral orders because they were not effectively
unreviewable after final judgment

[S]In addition, the courts of appeals can hear appeals

Apdx A - 5

from interlocutory orders granting, modifying, or dissolving
injunctions. [6]The district court's injunction concerned the
defendanis' liability under state nuisance and environmental
laws, not their liability under CERCLA. [7]The court of
appeals therefore had jurisdiction over the interlocutory order
finding the defendants liable under state law because it was
part of an order granting an injunction, but the CERCLA
order fell under none of the statutory provisions that allowed
for immediate interlocutory appeal.

{8]Furthermore, given criticism of pendent appellate
jurisdiction, and the consequent narrow construction of the
exception for "inextricably intertwined" rulings, the CERCLA
order was not inextricably intertwined with the state law
injunction

[9] The court of appeals lacked jurisdiction to hear the
CERCLA portion of the appeal.

{10]The defendants argued that the district court

Apdx A - 6

ae

should not have adjudicated their liability under state law

without giving them more time to conduct discovery. [11]
Litigants must submit affidavits setting forth the particular
facts expected from further discovery. [12]The record
showed that the defendants only implicitly moved for more
time to conduct discovery, an adequate ground for affirmance
of the district court's denial of their request for more
discov ery

[131In any event, denial of an application for
additional discovery is proper when it is clear that the
evidence sought was almost certainly nonexistent or was the
object of pure speculation. [14]Given uncontroverted facts
regarding trichloroethylene dumping and contamination, the
evidence sought, concerning another source of groundwater
contamination, was almost certainly nonexistent or was the
object of pure speculation

[15] Moreover, a party seeking a continuance for

Apdx A - 7

additional discovery must show that it lacks the facts essential

to resist the summary judgment motion. [16]The undisputed
evidence that trichloroethylene contaminated the soil and
groundwater was sufficient to establish liability under
California law Any additional data about contamination at
other property was not relevant to oppose the summary
adjudication motion. [17]The district court did not abuse its
discretion when it denied defendants’ request to stay summary
adjudication and continue discovery

[18]The defendants also argued that there were
genuine issues of material fact about who polluted the
groundwater at locations downgradient from company
property. The relevant inquiry in a summary adjudication
motion is threefold’ is there a genuine issue, 1s that issue
about a material fact, and is the moving party entitled to
judgment as a matter of law

[19]An issue of fact is genuine if the evidence is such

Apdx A -8

that a reasonable jury could return a verdict for the nonmoving

party. [20|The testimony of the defendants’ expert witness
(21] suggested that Louisiana Pacific Property was the source
of the trichloroethylene contamination. [22]However, given
the undisputed facts of trichloroethylene use and
contamination on Victor property, the only reasonable
conclusion to be drawn from the expert's evidence was that
the trichlorocthylene must have flowed from downgradient
where it accumulated at the edge of the Louisiana Pacific
Property. Accordingly, there was no genuine dispute about
which property polluted the groundwater!

|23|The defendants failed to show that the parties
disputed material facts The facts pertaining to offsite
pollution were not material to California's summary
adjudication motion. [24]To state a claim under California
law. it was enough that the water itself was contaminated.

California did not have to prove that trichloroethylene

Apdx A - 9

migrated to other areas.

[25]Unlike CERCLA, California law imposes liability
on any person who maintains a nuisance-regardless of whether
that person has an interest in the land. As executors of
Muscat's estate and trustees over Muscat's trusts, the
appellants maintained a nuisance by administering property
where hazardous chemicals were polluting the water. They
were therefore liable under California law regardless of
whether they were owners or operators under CERCLA.

[26] The injunction that required the appellants to abate
the public nuisance was not overbroad. [27]Furthermore, the
district court independently reviewed the department's cleanup
order, from which the injunction was derived, and concluded
its provisions were necessary to ensure public safety.

[28]Ordinarily, an injunction should not incorporate
another document by reference. [29]By incorporating the

order into the injunction, the district court did not err. The

Apdx A - 10

i

defendants received adequate notice that they could face
contempt if they violated because it was physically attached to

the injunction

COUNSEL

Sandra Goldberg, Deputy Attorney General, Oakland,
California, for plaintiff-appellee, State of California
Department of Toxic Substances Control

Dale C. Campbell, L. Burda Gilbert, Weintraub, Genshlea &
Sproul, Sacramento, California, for defendants-appellants
Albert Campbell and Charles Tackman, as Executors of the
Estate of Victor Muscat

Thomas H. Clarke, Jr., Susan H. Handelman. Ropers, Majeski,
John & Bentley, Redwood City, California, for intervenor

Western Resources. Inc

OPINION
PREGERSON, Circuit Judge

For almost twenty years, Victor Industries

Apdx A- 11

contaminated groundwater by dumping hazardous chemicals
onto the ground at its manufacturing plant. The State of
California sued the defendants under state environmental and
nuisance law to require them to clean up the contaminated
water. California also sought reimbursement from the
defendants under the Comprehensive Environmental
Response, Compensation, and Liability Act ("CERCLA"), 42
U.S.C § 9601, et seq., for the money that California spent
investigating the contamination.

Two of the defendants-Albert Campbell and Charles
Tackman-appeal the district court's orders finding the
defendants name under CERCLA and California law
Campbell and Tackman also appeal the district court's
injunction requiring the defendants to clean up the
contaminated water

Because we have no jurisdiction to review the district

court's interlocutory order finding the defendants liable under

Apdx A - 12

CERCLA, we dismiss that portion of the appeal. We have
junsdiction over the remainder of the appeal under 28 U.S.C
§ 1292(a)(1), and we affirm
BACKGROUND

Victor Muscat owned Victor Industries until his death
in 1974. From 1958 to 1984, Victor Industries manufactured
metal tubes and cans at a plant on 20th Street in Chico,
California ("the 20th Street Property"). For almost twenty
years, workers at the plant used trichlorocthylene as a solvent
and disposed of it by dumping it on the ground
Trichloroethylene is a hazardous substance that causes cancer

During an inspection, the California Department of
Toxic Substances Control ("the Department") noticed
hazardous substances stored in a manner that suggested that
the hazardous substances were being dumped at the 20th
Street Property. The Department took several soil samples

An analysis of the samples indicated the presence of

Apdx A - 13

‘An analysis of the samples indicated the presence of
trichloroethylene and other hazardous chemicals in the soil

Subsequent testing indicated that high concentrations
of trichloroethylene and other hazardous substances were
present not only in the soil but also in the groundwater at the
20th Street Property. The Department tested the groundwater
in municipal and private wells that are located downgradient
from the 20th Street Property and determined that
trichloroethylene had contaminated that groundwater as well.
One of the polluted wells was located at Stanley Park, a
housing subdivision located about a mile downgradient from
the 20th Street Property.

On behalf of the Department, the State of California
filled a complaint in federal court to require the defendants to
clean up the contamination and to recover the money that the
Department had spent investigating the contamination. The

complaint named as defendants the executors of Muscat's

Apdx A - 14

estate and the trustees of Muscat's testamentary trusts. |
California moved for summary adjudication of three of
its six claims: a federal environmental claim under CERCLA.
42 U.S.C. § 9601, et seq.; a state public nuisance claim under
California's common law; and a state environmental claim
under California's Hazardous Substance Account Act, Cal
Health & Safety Code § 25300 et seq. Specifically, California
argued that the defendants were liable as a matter of law for
violating both CERCLA and the state laws. As a remedy for
the state law violations, California requested a permanent
injunction requiring the defendants to abate the public
nuisance that the tnchloroethylene contamination had caused

In opposition to California's motion, the defendants

‘After California filed this lawsuit. the Connecticut Superior
Court. which oversaw Muscat's estate. removed the trustees and
placed the trust assets into receivership. The federal court in
California then substituted Western Resources. Inc., the appointed
receiver. as a defendant in place of the trustees. Western Resources
intervened in this appeal and filed a brief in support of the appellants’
arguments

Apdx A - 15

—

argued that the trichloroethylene detected at Stanley Park and
the other off-site locations did not come from the 20th Street
Property. The culprit, the defendants argued, was property
owned by Louisiana Pacific ("the Louisiana Pacific Property"),
which is located about a half-mile downgradient from the 20th
Street Property and about a half-mile upgradient from Stanley
Park.

The district court granted California's motion in its
entirety, and the defendants appealed.”

STANDARDS OF REVIEW

We review grants of summary adjudication motions de
novo. Amdahl Corp. v. Profit Freight Systems, Inc., 65 F 3d
144, 146 (9th Cir. 1995). The district court's ability to grant
an injunction is reviewed de novo, but the district court's

exercise of that power is reviewed for abuse of discretion.

“Western Resources appealed separately. Its appeal is
therefore discussed in a Separate opinion, which is found at
California v. Campbell, ___ F.3d (9th Cir. 1998).

Apdx A - 16

‘

Continental Airlines, Inc. v. Intra Brokers, Inc., 24 F.3d
1099, 1102 (9th Cir. 1994)
DISCUSSION

Under California law, those responsible for polluting
groundwater can be held liable for creating a public nuisance
and for violating California's environmental laws. See Carter
v. Chotiner, 210 Cal. 288, 291 (1930) (polluted water is a
public nuisance); Se/ma Pressure Treating Co., Inc. v. Osmose
Wood Preserving Co., 221 Cal. App. 3d 1601, 1616-20
(1990) (any person who creates or helps create and maintain
a nuisance is liable for its abatement and damages), Cal
Health & Safety Code § 25358.3 (those responsible for
endangering the public's health or safety or the environment
may have to take remedial action to protect the public and the
environment). Under CERCLA, any person who owned or
operated a facility when hazardous substances were disposed

there is liable for the costs that the government incurs when it

Apdx A- 17

a

responds to the contamination. 42 U.S.C. § 9607(a) ("any
person who at the time of disposal of any hazardous substance
owned or operated any facility at which such hazardous
substances were disposed of shall be liable for. . . all
costs of removal and remedial action incurred by the United
States Government or a State. ___.")

The district court found that the defendants were liable
under both California law and CERCLA and granted
California's motion for summary adjudication. As a remedy
for the defendants’ violations of California law. the district
court issued an injunction that requires the defendants to
abate the nuisance caused by the trichloroethylene
contamination
fe The defendants argue that the summary adjudication
was improper because they did not have enough time to
discover facts that were necessary to oppose the motion and

because California failed to meet the summary adjudication

Apdx A - 18

standards. The defendants also argue that the injunction was

improper because it is too broad and because it unlawfully
incorporates a document by reference
[| Jurisdiction

[1]Before we address these issues on the merits, we

must determine that we have jurisdiction to do so. As a

general rule, federal courts of appeal have jurisdiction only

over final decisions of the district courts. See 28 U.S.C. §

1291 (granting federal appellate courts "jurisdiction of appeals
from all final decisions of the district courts"). A final decision
is one that "ends the litigation on the merits and leaves nothing
for the court to do but execute the judgment." (at/in v.
United States, 324 U.S. 229, 233 (1945) (citing St. Louis 1.4
& S.A. v. Southern Express Co., 108 U.S. 24, 28 (1883))
Accordingly, an order that determines liability but not

damages ts not a final decision, /n re Frontier Properties, Inc..,

979 F.2d 1358. 1362 (9th Cir. 1992). nor is an order that

Apdx A - 19

adjudicates less than all claims a final decision, Chacon v.
Babcock, 640 F.2d 221, 222 (9th Cir. 1981)

[2] The orders that the appellants appeal are precisely
such orders. The CERCLA order determined that the
defendants were liable under CERCLA for the costs that
California incurred while investigating the contamination at
the 20th Street Property, but it did not determine what those
costs were. The state-law order resolved the nuisance and
endangerment-to-the environment claims, but left several
other claims unresolved. Thus, unless the summary
adjudication orders fall under an exception to the final
judgment rule. we have no jurisdiction to bear them.

A. Collateral Order Doctrine

[3] The Supreme Court has recognized that "§ 129]
permits appeals not only from a final decision by which a
district court disassociates itself from a case, but also from a

small category of decisions that, although they do not end the

Apdx A - 20

litigation, must nonetheless be considered 'final’." Swint v.
Chambers County Comm'n, 514 U.S. 35, 42 (1995) (citing
Cohen v. Beneficial Indus. Loan Corp., 337 U.S. 541. 546
(1949)). This small category of decisions “includes only
decisions that are conclusive, that resolve important questions
separate from the merits, and that are effectively unreviewable
on appeal from the final judgment in the underlying action."
Id. (citing Cohen, 337 U.S. at 546)

[4] The summary adjudication orders establishing the
defendants: CERCLA and state law liability are not among this
small category of decisions because they do not satisfy the last
factor of the test: they are not effectively unreviewable after
final judgment. As the Supreme Court explained in Swint, “an
erroneous ruling on liability may be reviewed effectively on
appeal from final judgment." Swint, 514 U.S. at 43
Accordingly, the orders granting California's summary

adjudication motions are not appealable collateral orders

Apdx A - 21

B. Statutorily-Appealable Interlocutory Orders

[5]In addition to final decisions and the small category
of cases that must be considered final under the collateral
order doctrine, federal appellate courts have jurisdiction over
four types of interlocutory decisions. The courts of appeal can
bear appeals from interlocutory orders granting, modifying, or
dissolving injunctions; interlocutory orders appointing
receivers or refusing orders to wind up receiverships,
interlocutory orders determining the nghts and liabilities of the
parties to admiralty cases, and interlocutory orders that the
district court certifies for immediate appeal because the orders
are pivotal and debatable. See 28 U.S.C. § 1292.

The district court did not certify the CERCLA order
or the state law order for immediate appeal, and neither order
concerns receiverships or admiralty. Thus, to fall under the

Statutory provisions allowing immediate appeal of

interlocutory orders, the summary adjudication orders must be

Apdx A - 22

BEA OS Battlin cdn Po 4

orders "granting, continuing, modifying, refusing or dissolving
injunctions." 28 U.S.C. § 1292(a)(1)

(6]After finding the defendants liable for creating a
public nuisance and violating California's en\ ironmental laws.
the district court issued an injunction requiring the defendants
to abate the public nuisance that the trichloroethylene
contamination had caused. Although the district court found
that the defendants were also liable for California's
investigation costs under CERCLA, it did not issue an
injunction that required the defendants to reimburse California
Thus, the injunction that the court issued concerned the
defendants’ liability under state nuisance and environmental
laws, not their liability under CERCLA

[7]We therefore have jurisdiction over the
interlocutory order finding the defendants liable under state
law because it is part of an order granting an injunction. The

interlocutory order finding the defendants liable under

Apdx A - 23

CERCLA, on the other hand, is not part of the order granting
the injunction. The CERCLA order therefore falls under none
of the statutory provisions that allow for immediate
interlocutory appeal
C. Pendent Appellate Jurisdiction

The defendants argue that the CERCLA order is
nevertheless appealable because it is "inextricably intertwined"
with the injunction They invoke the doctrine of pendent
appellate jurisdiction that the Supreme Court alluded to in
Swint v. Chambers County Commission, 514 US. 35 (1995)

Swint was a civil rights case against the Chambers
County Commission and three police officers. The police
officers argued that they were entitled to qualified immunity,
and the Commission argued that it was not liable because the
sheriff who authorized the alleged civil rights violations was
not the county's final policy-maker. The district court

summarily adjudicated both parties' defenses and found that

Apdx A - 24

neither party was entitled to judgment

Both parties immediately appealed even though the
district court had not issued a final judgment. The Eleventh
Circuit held that it had jurisdiction over the police officers’
appeal under Mitchell v. Forsyth, 472 U.S. 511, 530 (1985),
which held that an order denying qualified immunity is
immediately appealable. The Eleventh Circuit then held that
it had pendent appellate jurisdiction over the Commission's
claims even though the Commission's claims were not
independently appealable

The case then came before the Supreme Court. The
Court agreed that the Eleventh Circuit had jurisdiction over
the police officers’ appeal, but held that "the Circuit Court did
not thereby gain authority to review the denial of the
Chambers County Commission's motion for summary
judgment.” Swit, 514 U.S. at 38. In other words, "there [was

no| ‘pendent party’ appellate authority to take up the

Apdx A - 25

Commission's case." Id -

In so holding, the Court noted that the federal courts
of appeals have endorsed the doctrine of pendent jurisdiction.
ld. at 44 n2. The Court also acknowledged the parties’
argument that § 1291's final decision requirement is designed
to prevent parties from interrupting litigation by pursuing
piecemeal appeals and that once litigation has already been
interrupted by an authorized pretrial appeal, there is no cause
to resist the economy that pendent jurisdiction promotes. /d
at 45

But the Court stated that. "[t]hese arguments drift
away from the statutory instructions Congress has given to
control the timing of appellate proceedings." Jd If courts of
appeals had discretion to hear "pendent" appeals, then
Congress’ statutory arrangement would be undermined. /d. at
45-48 (discussing 28 U.S.C. § 1292. which lists certain

interlocutory appeals that are immediately appealable, and §

Apdx A - 26

2072(c) of the Rules Enabling Act. 28 USC § 2071 et seq..
which grants the Supreme Court rulemaking authority to
proscribe which interlocutory orders are appealable)

Despite this strong language against pendent appellate
jurisdiction, the Court left open a loophole for "inextricably
intertwined" rulings. The Court stated that it “need not
definitively or preemptively settle here whether or when it may
be proper for a court of appeals with jurisdiction over one
ruling to review. conjunctively, related rulings that are not
themselves independently appealable." /d. at 50-51. The
Court noted that the parties did "not contend that the District
Court's decision to deny the Chambers County Commission's
summary judgment motion was inextricably intertwined with
that court's decision to deny the individual defendants’
qualified immunity motions." /d. at 51. Nor. the Court noted,
did the parties contend that "review of the former decision

Was necessary to ensure meaningful review of the latter." Jd

Apdx A - 27

[8]Given the Supreme Court's criticism of pendent
appellate jurisdiction, the Court's "inextricably intertwined"
exception should be narrowly construed. Under such a
construction, the CERCLA order is not inextricably
intertwined with the injunction. As explained above, the
district court granted the injunction to abate the public
nuisance that was caused by the trichloroethylene
contamination at the 20th Street Property. We can easily
address the defendants’ state law liability without discussing
the defendants’ CERCLA liability. Just because the same facts
are involved in both issues does not make the two issues
inextricably intertwined. See Swint, 514 U.S. 35: United
States v. Stanley, 483 U.S. 669, 676-78 (1987); Abney v.
United States, 431 U.S. 651, 662-63 (1977) (all holding that
appellate court with interlocutory jurisdiction over one ruling

lacked jurisdiction to review factually-related rulings that were

not independently appealable).

Apdx A - 28

|
— s
—-

[9]In sum, the interlocutory CERCLA order does not
tall under the collateral order doctrine, the interlocutory-
appeal statute, or the "inextricably intertwined" doctrine. We
therefore lack jurisdiction to hear the CERCLA portion of this
appeal. Accordingly, we will now turn to the portions of the
appeal over which we do have jurisdiction: the appeal from the
district court's order finding the defendants liable under state
law and the appeal from the district court's order issuing an
injunction against the defeindants

Il. Summary Adjudication of the Defendants’
Liability Under State Law
A. Sufficient Time for Discovery

[10]The defendants first argue that the district court
should not have adjudicated their liability under state law
without giving them more time to conduct discovery. They
rely on Rule 56(f) of the Federal Rules of Civil Procedure.

vhich states as follows

Apdx A - 29

Should it appear from the affidavits of a party
opposing the motion that the party cannot for
reasons stated present by affidavit facts essential

to justify the party's opposition, the court may

refuse the application for judgment or may order

a continuance to permit affidavits to be obtained

or depositions to be taken or discovery to be had

or may make such other order as is just.

District courts have "wide latitude in controlling
discovery, and [their] rulings will not be overturned in the
absence of a clear abuse of discretion." Volk v. D.A. Davidson
& Co., 816 F.2d 1406, 1416-17 (9th Cir. 1987) (quoting
Foster v. Arcata Assoc., Inc., 772 F.2d. 1453, 1467 (9th Cir
1985)). Nevertheless, a district court should continue a
summary judgment motion upon a good faith showing by
affidavit that the continuance is needed to obtain facts

essential to preclude summary judgment. See McCormick v.

Apdx A - 30

lund American Cos., Inc., 26 F.3d 869, 885 (9th Cir. 1994)
Thus, the defendants must show (1) that they have set forth in
affidavit form the specific facts that they hope to elicit from
further discovery, (2) that the facts sought exist, and (3) that
these sought after facts are "essential" to resist the summary
judgment motion
1. Affidavits

[11]"References in memuranda and declarations to a
need for discovery do not qualify as motions under Rule
56(f)." Brae Transp., Inc. v. Coopers & Lybrand, 790 F.2d
1439, 1443 (9th Cir. 1986). Rather, Rule 56(f) requires
litigants to submit affidavits setting forth the particular facts
expected from further discovery. We have stated that
"[fJailure to comply with the requirements of Rule 56(f) is a
proper ground for denying discovery and proceeding to
summary judgment." /d.

[12] The record does not show whether the defendants

Apdx A - 31

ever actually submitted affidavits setting forth the particular
evidence that they had hoped to elicit from further discovery
lt appears from the record that the defendants only implicitly
moved for more time to conduct discovery. For instance.
when addressing the defendants’ request for an extension of
time, the district court did not refer to any specific motion by
the defendants. Instead, the district court stated that the
‘[dJefendants imply that they will request further time for
discovery of the facts upon which plaintiff bases its motion."
The defendants’ apparent noncompliance with the terms of the
statute provides an adequate ground for us to affirm the
district court's denial of the defendants’ request for more
discovery. See id.
2. Existence of Facts Sought
[13]In any event, as we have emphasized. "[djenial of

a Rule 56(f) application is proper where it is clear that the

evidence sought is almost certainly nonexistent or is the object

Apdx A - 32

of pure speculation." 7erre// v. Brewer, 935 F.2d 1015, 1018
(9th Cir. 1991)

[14]Here, the defendants wanted more time to
discover the source of the groundwater contamination at
Stanley Park. There is undisputed evidence, however, that
workers at Victor Industries dumped trichloroethylene at the
20th Street Property for almost twenty years, that
groundwater under the 20th Street Property is contaminated
with trichloroethylene, that a well located between the 20th
Street Property and the Louisiana Pacific Property is
contaminated with trichloroethylene, that the Louisiana Pacific
Property is not contaminated with trichloroethylene, and that
the groundwater is flowing from the 20th Street Property
toward Stanley Park. Given these uncontroverted facts.
evidence that the 20th Street Property was not the source of
contamination at Stanley Park is almost certainly nonexistent

or is the object of pure speculation." /d

3. Essentialness of Facts Sought

[15]Moreover, Rule 56(f) mandates that "the party
seeking the continuance must show that it lacks the ‘facts
essential’ to resist the summary judgment motion."
McCormick, 26 F 3d at 885. But the facts that the defendants
hope to elicit during discovery are not essential to resisting
California's summary adjudication motion

[16] The undisputed evidence that trichloroethylene
contaminated the soil and groundwater at the 20th Street
Property is sufficient to establish the defendants’ liability under
California law. To succeed on its summary adjudication
motion, California need not prove that property other than the
20th Street Property suffered from contamination Under
California law, the pollution at the 20th Street Property
constitutes a public nuisance and violates California's
environmental laws. See Carter v. Chotiner, 210 Cal. 288.

291 (1930) (polluted water is a public nuisance); Cal. Health

Apdx A - 34

3
:

ee ae ee’ a en

& Safety Code § 253583 (when a release or threatened
release of hazardous substances endangers the environment,
those responsible may have to take remedial action)
Therefore. any additional data about contamination at
property other than the 20th Street Property is not relevant to
oppose the summary adjudication motion. See McCormick,
26 F.3d at 885 (concluding that additional testimony "would
have made no difference on suminary judgment, because the
allegedly omitted maternal would not have altered the total mix
of information available" to the plaintiff)

[17]The defendants therefore have not satisfied the
requirements of Rule 56(f). Accordingly, the district court did
not abuse its discretion when it denied the defendani's request
to stay summary adjudication and continue discovery

B. Summary Adjudication Standards
[18]Next, the defendants argue that there are genuine

issues Of material fact about who polluted the groundwater at

Apdx A - 35

Stanley Park and other off-site locations. They also argue that
California is not entitled to judgment as a matter of law
because the defendants were not owners or operators of the
20th Street Property. In short, the defendants believe that
California failed to meet the requirements for summary
adjudication

Summary adjudication "shall be rendered forthwith if
the pleadings, depositions, answers to interrogatories, and
admissions on file, together with the affidavits, if any, show
that there is no genuine issue as to any material fact and that
the moving party is entitled to a judgment as a matter of law."
Fed R. Civ. P. 56(c). “By its very terms, this standard
provides that the mere existence of some alleged factual
dispute between the parties will not defeat an otherwise
properly supported motion for summary judgment, the
requirement is that there be no genuine issue of material fact.”

Anderson v. Liberty Lobby, Inc., 477 U.S. 242, 247-48

Apdx A - 36

(1986). Thus. the relevant inquiry in a summary adjudication

motion is threefold: is there a genuine issue, is that issue
about a material fact, and is the moving party entitled to
judgment as a matter of law
|. Genuine Issue

{19} An issue of fact is genuine if the ev idence is such
that a reasonable jury could return a verdict for the nonmoving
party. Anderson, 477 US. at 248 Of course, there must be
sufficient evidence favoring the nonmoving party for a jury to
return a verdict for that party.” /d. at 249 (citing First Nat

Bank of Ariz. v. Cities Services, Co., 391 U.S. 253. 298-89

(1968). “If the evidence is merely colorable or is not
significantly probative summary judgment may be

granted." /d. at 249-50 (citations omitted)
[20]The defendants contend that the district court
erred by rejecting the testimony of Jay Lucas (their expert

witness) and the contour maps that Lucas prepared. The

Apdx A - 37

contour maps allegedly depict a "bull's eye" of
trichloroethylene contamination radiating from the Louisiana
Pacific Property. According to the defendants, Lucas's maps
and testimony support an inference that the Louisiana Pacific
Property was the source of the contamination detected at
Stanley Park.

[21] The Lucas evidence does create a dispute--or, in
the words of the summary adjudication statute, an "issue"--
between the parties: Lucas's evidence Suggests that the
Louisiana Pacific Property contaminated the water at Stanley
Park, and California's evidence Suggests that the 20th Street
Property contaminated the water at Stanley Park.

Merely showing that there is a dispute, however, is not
enough. The defendants musi show that there iS a genuine
dispute. This they have failed to do in the abstract, the
defendants are right. A juror who accepted Lucas's maps as

accurate could conclude that the contamination was

Apdx A - 38

.
i

originating from the Louisiana Pacific Property and was
becoming more diluted as it spread outwards. But this case
does not arise in the abstract. It arises in the context of
undisputed facts. many of which mandate a different
interpretation of Lucas's maps: namely, that the contamination
flowed "downhill" from the 20th Street Property and
accumulated at the bottom of the incline, which happened to
be at the edge of the Louisiana Pacific Property

[22]Given the following facts, no reasonable juror
could conclude that the Louisiana Pacific Property, rather than
the 20th Street Property, was the source of the contamination
at Stanley Park: (1) From 1963 to 1980, workers at Victor
Industries used large quantities of trichloroethylene as a
degreaser at the 20th Street Property and dumped it on the
ground there, (2) scientists detected trichloroethylene
contamination in the soil and in the water at the 20th Street

Property, (3) water flows from higher ground to lower

Apdx A - 39

ground. (4) the Louisiana Pacific Property is downgradient
from the 20th Street Property, (5) a well located between the
two properties -- in other words, downgradient from the 20th
Street Property and upgradient from the Louisiana Pacific
Property -- is contaminated with trichloroethylene: and (6)
testing of various sources of contamination at the Louisiana
Pacific Property revealed no trichloroethylene’* Thus. if
Lucas's maps were accurate and there really was more
trichloroethylene near the Louisiana Pacific Property than
there was away from it, then the trichloroethylene must have

flowed from the 20th Street Property and accumulated at the

‘The defendants argue that the Louisiana Pacific Property is
nor downgradient from the 20th Street Property and that the
Louisiana Pacific Property is polluted with trichloroethylene. They
have failed to present anv evidence to support these arguments.
however. Instead. they argue that thev necd more time to obtain such
evidence. As discussed above. this argument is not persuasive. The
defendants failed to file the necessary affidavit and they failed to
show that additional discovery would uncover essential facts. Thus.
although the court must view genuinely -disputed facts in the light
most favorable to the defendants. it must treat these unrebutted facts
as truc

Apdx A - 40

edge of the Louisiana Pacific Property. No other conclusion
is reasonable given the undisputed facts of this case.
Accordingly, there is no genuine dispute about which property
polluted the water at Stanley Park and the other off-site
locations
2. Material Fact

[23]Besides failing to show a genuine dispute, the
defendants fail to show that the parties dispute material facts
The defendants list many facts that the parties dispute, but as
the defendants themselves point out, all of the disputed facts
pertain to how the trichloroethylene ended up at Stanley Park
and other off-site locations. As shown below. the facts
pertaining to off-site pollution are not material to California's
summary adjudication motion

Substantive law determines which facts are material
Anderson, 477 U.S. at 248. "Only disputes over facts that

might affect the outcome of the suit under the governing law

Apdx A - 41

-—

will properly preclude the entry of summary judgment.

Factual disputes that are irrelevant or unnecessary will not be

counted." /d.

The relevant substantive law here is California
nuisance law and California environmental law. Under these
laws, polluted water is a public nuisance, Carter v. Chotiner.
210 Cal. 288, 291 (1930), and any person who creates or
helps create and maintain a nuisance is liable for its abatement
and damages. Se/ma Pressure Treating Co., Inc. v. Osmose
Wood Preserving Co., 221 Cal. App. 3d 1601, 1619-20
(1990). Furthermore, when a release or threatened release of
hazardous substances endangers the environment. those
responsible may be ordered to take remedial action. Cal.
Health & Safety Code § 25358 3.

[24]Thus, to state a claim under California law.
California need not prove that trichloroethylene migrated from

the 20th Street Property to other areas. It is enough that the

Apdx A - 42

Pre ee ee

water under the 20th Street Property itself was contaminated

in other words, the polluted water at the 20th Street Property
created a public nuisance and endangered the environment.
The cause of the trichloroethylene contamination at Stanley
Park and other off-site areas is therefore immaterial to
California's state law claims.
3. Judgment as a Matter of Law

Given that there is no genuine dispute about any
material fact, the defendants can defeat the summary
adjudication order only if the facts do not entitle California to
judgment as a matter of law. See Fed. R. Civ. P. 56(c)
(summary judgment is appropriate when there is no genuine
issue of material fact and the moving party is entitled to
judgment as a matter of law). The defendants argue that
California is not entitled to judgment as a matter of law
because the defendants were not owners or operators of the

20th Street Property at the time that hazardous chemicals

Apdx A - 43

were disposed there

This argument presumably goes to the interlocutory
CERCLA-liability issue, over which we have no appellate
jurisdiction. As mentioned above, it is CERCLA-not state
law-that imposes liability on "owners" and "operators" of
facilities at which hazardous substances were dumped. 42
U.S.C. § 9607

[25]Unlike CERCLA, California law imposes liability
on any person who maintains a nuisance--regardless of
whether that person has an interest in the land. Hardin v. Sin
Claire, 115 Cal. 460, 463-64 (1896) (holding administrator of
an estate liable for maintaining a nuisance even though it was
the decedent who had originally created the nuisance). As
executors of Muscat's estate and trustees over Muscat's trusts.
the appellants maintained a nuisance by administering property
where hazardous chemicals were polluting the water.

Therefore, the appellants are liable under California law

Apdx A - 44

regardless of whether they were owners or operators under
CERCLA. Accordingly, the district court properly found that
California was entitled to judgment as a matter of law on the
state law claims

California has met the requirements for summary
adjudication. The district court therefore did not err when it
found as a matter of law that the defendants were liable under
California's nuisance and environmental laws:

Ill. Issuance of the Injunction

Besides contesting their liability under state law, the
defendants contest the injunction that requires them to abate
the public nuisance. Specifically, the defendants argue that the
injunction is too broad and that it violates Rule 65(d) of the
Federal Rules of Civil Procedure

A. Breadth of Terms
[26] Although the defendants claim that the entire

injunction is overbroad, they point to only two provisions that

Apdx A - 45

ihey claim are too broad: the modification provision (which
allows the State Department of Toxic Substances Control to
modify an order that it issued) and the waterline provision
(which requires the defendants to install a waterline to Stanley
Park). The modification provision, however, is not part of the
injunction,’ and the waterline provision is moot because
California has already built the waterline, see Friends of the
Earth, Inc. v. Bergland, 576 F.2d 1377, 1379 (9th Cir. 1978)

("Where the activities’ sought to be enjoined have already

‘Although the modification provision is part of an order that
Was incorporated into the injunction, the district court specifically
excepted that provision front the injunction:

If the State construes my order as incorporating [the
modification provision] . . . . it seems to me that |the
modification provision] . . . provides the Executive
Branch with authority to engage in unilateral action. |
don't think that the Executive Branch should have the
authority to engage in such action ... and | have no
intention of embracing such action.

Any action that is before me for purposes of contempt
must be on the basis of something that | have
specifically ordered

Apdx A - 46

— OO eee, 2.

occurred, and the appellate courts cannot undo what has
already been done, the action is moot."). Moreover, the
remaining provisions of the injunction are not overbroad

The provisions of the injunction originate from an
order that requires the defendants to clean up soil and water
at the 20th Street Property and at areas up to a mile away
The order was issued by the State Department of Toxic
Substances Control. The Department of Toxic Substances
Control has experience removing hazardous substances from
the soil and is authorized by the California Health and Safety
Code to issue orders for removing or remedying releases of
hazardous substances

[27|The district court independently reviewed the
provisions of the Department's order and concluded that they
were necessary to ensure public safety. The defendants might
believe that the provisions pertaining to the surrounding areas

are too broad because the 20th Street Property was not the

Apdx A - 47

source of the contamination detected at those areas. As
explained above, however, the district court properly found
that the 20th Street Property was the source of the off-site
contamination. The distnct court was therefore well within its
discretion when it relied on the Department's expertise and
incorporated the provisions of the order into the injunction
B_ Incorporation by Reference

[28]In their final argument, the defendants contend
that the distnct court violated, Federal Rule of Civil Procedure
65(d) by incorporating the Department's order into the
injunction Rule 65(d) provides that every order granting an
injunction “shall describe in reasonable detail, and not by
reference to the complaint or other document, the act or acts
sought to be restrained " Fed R. Civ. P. 65(d)
Ordinanly, “an injunction should not incorporate by reference
another document" Davis v. City and County of San

Francisco, 890 F 2d 1438, 1450 (9th Cir. 1989) (quoting

Apdx A - 48

Henry Hope X-Ray Prods., Inc. v. Marron Carrel, Inc., 674
F 2d 1336, 1343 (9th Cir. 1982))

We have not read Rule 65(d) so strictly as to preclude
any incorporation, however. See id. at 1450. Instead. we
have interpreted the rationale behind the incorporation-by-
reference language in Rule 65(d) as a safeguard to “ensure
adequate notice to defendants of the acts prohibited." Henry
Hope X-Ray, 674 F.2d at 1343 (holding that the district court
did not abuse its discretion when it failed to attach a
confidential appendix to its injunctive order because the
appendix was transmitted to the parties)

[29]By incorporating the order into the injunction, the
district court acted consistently with the rationale of Rule
65(d). The defendants were aware of the order because it was
physically attached to the injunction itself | Thus. the
defendants received adequate notice that they could face

contempt if they violated the order Under these

Apdx A - 49

circumstances, the district court did not err by attaching the
order to the injunction
CONCLUSION

[he district court properly found the defendants liable under
California's nuisance and environmental laws and propert\
issued an injunction against the defendants Given
interlocutory posture of this case. however. we lack appe
jurisdiction to consider whether the district court also pr
found the defendants liable for California's clean-up costs

under CERCLA Accordingly. the CERCLA portion of this

appeal 1s DISMISSED and the remainin

appeal are AFFIRMED

APPENDIX B

UNITED STATES DISTRICT COURT
FOR THE
EASTERN DISTRICT OF CALIFORNIA

IN THE UNITED STATES DISTRICT COURT
FOR THE EASTERN DISTRICT OF CALIFORNIA

STATE OF CALIFORNIA.) CV S-93-604 GEB/JFM
on behalf of the California ) ORDER
Department Toxic )
Substances )
Control
Plaintiff,
\ )
ALBERT CAMPBELL.
individually and Trustee

of the VICTOR MUSCAT
TESTAMENTARY TRUSTS)

and Executor of the )
ESTATE OF VICTOR
MUSCAT, CHARLES )
TACKMAN, individually
and as Trustee of
the VICTOR MUSCAT )

TESTAMENTARY TRUSTS)
and Executor of the ESTATE)
OF VICTOR MUSCAT

Defendants

Plaintiff moves for partial summary judgment on three

of its six claims. Its first claim seeks recovery of costs it

Apdx B - 51

incurred to cleanup a release of hazardous substances under
the Comprehensive Environmental Response, Liability and
Compensation Act, 42 U.S.C. 9601, et seq. ("CERCLA").
Plaintiff seeks a determination that Trustees Campbell and
Tackman are strictly liable as owners or operators for the
release and threatened release of PCE and TCE from a factory
operated by Victor Industries at 265 East 20th Street in
Chico, California ("the 20th Street property"). Defendants
argue that although trichloroethylene ("TCE") and
perchloroethylene ("PCE") were released into the soil on the
20th Street property, plaintiff fails to prove Victor Industries
caused the contamination of groundwater drinking water wells
at a housing subdivision called Stanley Park, a mile
downgradient from the Trust's property. Defendants claim
that the Louisiana-Pacific site between the 20th Street
property and Stanley Park also released PCE and TCE that

may have caused the contamination. Plaintiff also moves for

Apdx B - 52

entry of a permanent injunction on their second and third

claims for relief, The second claim is under a new California
3 environmental law, Health and Safety Code § 253583. The
third claim is for public nuisance

When defendants filed their opposition to the State's
motions, they also moved to dismiss the state law claims for
lack of subject matter jurisdiction. While the issue of subject
matter jurisdiction has not been fully briefed at this time,
plaintiff's motion, if granted would dispose of two of its state
law claims. Therefore, although defendants simply refer to
this issue in their briefs, delaying ruling until September 13,
1993, would render defendants, motion moot as to plaintiff's
State statutory and public nuisance claims. Plaintiff's claims
for clean-up of the TCE and PCE contamination at the 20th
Street site, and contamination migrating from that site, are
part of a single "case or controversy" within the supplemental

jurisdiction of this court. Defendants’ motion requests that

Apdx B - 53

this court exercise its discretion to dismiss the state claims,
and does not challenge the existence of subject matter
jurisdiction. Therefore, defendants' subject matter jurisdiction
arguments are rejected for this motion

A Mouon for Summary Judgment on Plaintiffs

“ERCLA claim

wy

It is undisputed that large quantities of PCE and TCE
were used as a degreaser by Victor Industries from 1963 to
1980 and released onto the ground at the 20th Street site.
TCE was found in tests of soil and soil gas and in shallow and
intermediate groundwater at that location

The potential dispute is whether plaintiff has
adequately proved that the TCE contaminating the
intermediate groundwater was caused by a release from the
, :
20th Street site Defendants assert that the Louisiana-Pacific |

property (""L-P") located between the 20th Street site and the

housing subdivision was the source. The evidence shows that

Apdx B - 54

CO re a

OE” BT ID Pee DERN

the intermediate groundwater flows in a west-southwest

direction and that wells monitoring the intermediate
groundwater on the east border of the L-P property show
PCE contamination. This is evidence that the intermediate
groundwater is contaminated before it reaches the L-P
property. Moreover, L-P conducted extensive soil and soil
gas studies of the various potential contamination sources and
found no TCE. Defendants argue that the burn pit on the
eastern edge of the L-P property should be investigated for the
presence of TCE. However CE and PCE are volatile organic
compounds not likely to be found in a burn pit area, as the
experts determined when conducting the initial investigation
and evaluation of the L-P site

Defendants attempt to show that L-P ts the source of
the TCE contamination using contour maps. However,
defendants’ expert used CE concentrations from various

depths of water to construct a contour map of the

Apdx B - 55

intermediate groundwater. Thus, defendants’ experts contour
maps cannot be accorded evidentiary weight.

Plaintiff has carried its burden of proving the elements
of its CERCLA claim as follows:

(1) the 20th Street site is a “facility,”

(2) TCE and PCE are “hazardous substances"
under CERCLA,

(3) a "release" and "threatened release" of
hazardous substances from the 20th Street site into the
environment has occurred and is occurring,

(4) plaintiff incurred costs for actions taken in
response to the release and threatened release of hazardous
substances from the 20th treet site,

(S) Campbell and Tackman, as Trustees of the
Victor Muscat Testamentary Trusts and as Executors of the
Estate of Victor Muscat are "owners" and were "operators" of

the 20th Street site at the time of disposal of the hazardous

Apdx B - 56

substances, and

(6) Campbell and Tackman are jointly and
severally liable for Plaintiff's costs of responding to the release
and threatened release of hazardous substances from the site
B Request for Permanent Injunction

Plaintiff also seeks a permanent injunction requiring
Campbell and Tackman, as Trustees of the Victor Muscat
Testamentary Trusts and as Execu.ors of the Estate of Victor
Muscat, to comply with its Imminent and Substantial
Endangerment and Remedial Action Order ("ISE Order") for
the 20th Street site, issued May 1992.' This order requires
defendants to install a drinking water line in the Stanley Park

subdivision, among other actions. Defendants have asserted

Following oral argument. Defendants submitted a proposed
order which would require them to install the drinking water line and
which they have argued would obviate the need for entry of a
permanent injunction. However. Defendants’ assurances of voluntary
compliance do not prevent entry of an injunction Securities &
Exchange Com'n y_ Murphy, 626 F 2d 633. 655-56 (9th Cir. 1980)

Apdx B - 57

they are unable to commit Trust funds for this purpose
without a authorization of the Connecticut Probate Court
which oversees the Testamentary Trusts. Thus the State
contends that defendants have failed and refused to comply
with the ISE Order and seeks injunctive elief under both the
California Hazardous Substance Account Act ("HSAA"), Cal.
Health and Safety Code §§ 25300 et seg., and public nuisance
law.* Defendants assert that their contour maps of the TCE
plume and the alleged lack of complete data create a disputed
issue of fact as to whether the TCE plume is an imminent and
substantial endangerment or was caused by defendants. These
arguments are rejected for the reasons stated above in the
summary judgment discussion.

Defendants next argue that the drinking line is not

“Defendants asserted in ora! argument that § 25366 which
bars liability for actions which were lawful before 1982 would apply
to the claim under Health and Safety Code § 25358. The court need
not decide this issue. as the plaintiff's public nuisance claim seeks
identical relief.

Apdx B - 58

Te ers

Git By,

Pb RAE MSEC RAS at EE ESE AS

necessary since they have installed Point of Entry Treatment

Systems ("POETS") on any well which was found to have
TCE above the Maximum Contaminant Level ("MCL") of 5.0
parts per billion for TCE in public drinking water supplies
Plaintiff argues in rebuttal that installation of the POETS is not
sufficient to prevent endangerment to public health. Plaintiff
points to evidence that the number of wells requiring
treatment systems has increased by two a year which
represents approximately a 25% increase per year. Moreover,
in tracking the TCE plume, defendants’ monitoring wells have
found increases in TCE concentration in just one month,
indicating that the quarterly monitoring of drinking water in
Stanley Park is not sufficient to protect residents from
exposure to levels of TCE above the MCL. Moreover,
defendants’ installation of the POETS does not avoid health
risks because the exposure to hazardous chemicals occurs for

another one to three months after detection of TCE levels

Apdx B - 59

above the MCL Furthermore, defendants do not conduct
regular testing of the POETS after installation to insure that
they are still effective

Plaintiff has shown that the drinking water line is
necessary to protect the health and safety of the residents of
Stanley Park, that POETS are not an effective alternative, and
that the plume has migrated su‘ficiently such that installation
of the dnnking water line is necessary before remediation can
occur. No other equitable considerations weigh significantly
into the determination. The Trustees argue that they face
potential suit by the trust beneficiaries if they expend funds for
the drinking water line without prior authorization by the
Connecticut Probate Court, however, they fail to consider the
potential health risks to residents of Stanley Park who are
unknowingly exposed to levels of TCE exceeding the MCL
caused by defendants failure to voluntarily comply with the

State's ISE Order.

Apdx B - 60

Therefore a permanent injunction is hereby issued
requiring defendants to abate the public nuisance of TCE and
PCE contaminated soil and groundwater at the 20th Street site
and the groundwater downgradient from the site. Defendants
shall abate the nuisance by complying with the State's ISE
Order of May 1992 (a copy of which is attached and
incorporated herein) with time limits or deadlines to apply
from the date of this Order and Injunction. -

IT IS SO ORDERED.

DATED: August 4, 1993

/s/ Garland E. Burrell, Ir

GARLAND E. BURRELL, JR

UNITED STATES DISTRICT JUDGE

Apdx B - 61

BEFORE THE CALIFORNIA
ENVIRONMENTAL PROTECTION AGENCY
DEPARTMENT OF TOXIC SUBSTANCES
CONTROL

In The Matter Of )
Former Victor Industries)
Corporation
operations at
365 E. 20th Street
Chico, California
Hazardous Waste Site

Responsible Parties

Victor Industries

Vic, Inc

Charles A. Tackman
and Albert F. Campbell
as trustees on behalf

of the Victor Muscat
Trust, CCL Industries,

Inc.. and Advanced

mee mem em me meme ee me me me meme ee”

Monobloc, Inc

Docket No. I/SE 91/92-007
IMMINENT OR
SUBSTANTIAL
ENDANGERMENT

AND REMEDIAL
ACTION ORDER

Health & Safety Code
(Sections 25358 5(a)(1)(B),

and 25358 .3(a)(1))

Apdx B - 62

Pe oe,

I INTRODUCTION

1.1 Parties The State Department of Toxic
Substances Control (Department) issues this Imminent or
Substantial Endangerment and Remedial Action Order (Order)
to Victor Industries; Vic, Inc., Charles A. Tackman and
Albert F. Campbell as Trustees on behalf of the Victor Muscat
Trust, CCL Industries, Inc. and Advanced Monobloc, Inc
(Responsible Parties).

1.2 Site. The Site which is the subject of this Order is
located at 365 East 20th Street in Chico, California. A map of
the Site is attached as Exhibit |

1.3 Jurisdiction Section 25355 5(a) (1) (B) of the
Health and Safety Code (H&SC) authorizes the Department
to issue an Order establishing a schedule for removing or
remedying a release of a hazardous substance at a site, or for
correcting the conditions that threaten the release of a

hazardous substance. The order includes, but is not limited to.

Apdx B - 63

requiring specific dates by which the nature and extent of a
release shall be determined and the site adequately
characterized, a remedial action plan prepared and submitted
to the Department for approval, and a removal or remedial
action completed This Order supersedes Remedial Action
Order Number HSA 88/89-0i4

1.3.1 Section 25358 3(a)(1) of the H&SC authorizes
the Department to order any responsible party to take
appropriate removal or remedial action if the Director
determines that there may be an imminent or substantial
endangerment to the public health or welfare or to the
environment because of a release or threatened release of a
hazardous substance and such removal or remedial action 1s
necessary

1 4 Exhibits All Exhibits attached to this Order are

incorporated herein by this reference

Apdx B - 64

Il FINDINGS AND DETERMINATIONS

2.0 Victor Industries; Vic, Inc. , Charles A. Tackman
and Albert F. Campbell as Trustees on behalf of the Victor
Muscat Trust; CCL Industries, Inc. and Advanced Monobloc,
Inc. are responsible persons or parties and liable persons as
defined by H&SC Sections 25323.5, 25319, 25360, and
| 25385. 1(g).

2.1 Description of Each Respondent and Connection
to Site

2.1.1 Victor Industries manufactured lead and
aluminum tubes and cans at 365 East 20th Street, Chico,
where they operated from approximately 1958 to 1985

Victor Industries used trichloroethylene (TCE) and
perchloroethylene (PCE) for degreasing and general cleaning.
Former employees have reported to the Department that these
solvents were disposed of by dumping them onto the ground

on the site The employees have stated that 150 to 200

Apdx B - 65

gallons of TCE were used each month the business was in
operation and that these substances were disposed of on the
site. It is estimated that 21,000 gallons of TCE and PCE were
dumped just during the seven year period from 1963 to 1970
These disposal practices have resulted in significant soil and
groundwater contamination

2.1.2 Vic, Inc. purchased Victor Industries in October
1984. Vic, Inc. is a successor corporation to Victor
Industries. Vic, Inc. is also an operator of the site because it
continued to manufacture tubes and cans at the site: until
approximately 1985. Vic, Inc. purchased and used PCE at the
site. PCE has been found in the soil and groundwater at the
site

2.1.3 The Victor Muscat Trust (Trust) is the present
land owner at the Site, and also owned the site during the time
that hazardous substances were disposed on the site.

2.1.4 CCL Industries, Inc. (CCL) and/or Advanced

Apdx B - 66

ee in lial

Monobloc, Inc. purchased Victor Industries in August, 1990
from Vic. Inc.. CCL and Advanced Monobloc, Inc. are

successor corporations to. Victor Industries.

22 Site Investigations and Substances Found at the
site
2.2.1 on September 15, 1984 the Department's

Surveillance and Enforcement Unit inspected the Victor
Industries’ East 20th Street facility and advised that certain
hazardous substances be removed from the Site. Samples
taken from the surface near the paint shed and next to the
doors on the southwest side of the manufacturing building
identified concentrations of TCE, PCE, 1,1,1 TCA, and
methylene chloride in the soil. During September 1985, 34
fifty-five gallon drums of excavated soil contaminated with
hazardous substances listed above, 33 cubic yards of asbestos

sheeting, and 21 drums of paint related material were removed

from the Site

» *&

2.2.2 Dunng September 1989 and January 1992, soil
gas samples were collected by the Department's contractor at
a depth of five feet at the Site The 1989 samples showed
concentrations of TCE at, 299 micrograms per liter (ug/1) in

the soil near the southwest doors of the old manufacturing

building. The 1989 samples also showed concentrations of

PCE at 113 ug/l near the old railroad tracks between the two
buildings on the site. Former Victor Industries’ employees
have identified these areas as disposal areas for hazardous
substances. The 1992 soil gas samples showed concentrations
of both TCE and PCE in soil beneath the plant slab, where
solvent degreasers used to operate’ TCE concentrations
exceeded 56 ug/l, and PCE exceeded 89 ug/I at this location
In addition, in December 1991 the Department collected a soil
sample at the same location as the 1989 soil gas samples,
which contained concentrations of TCE at 207,000 ug/l, and

PCE exceeding 2500 ug/I

Apdx B - 68

2.2.3 The Victor Muscat Trust hired Brown and
Caldwell consultants to perform investigations at the Site
during November, 1990 pursuant to the Department's
Remedial Action Order HSA 88/89-014. Brown and Caldwell
installed a groundwater monitoring well, and collected
groundwater samples at seven locations via the "hydropunch"
method. Six of these locations were downgradient and one
location was upgradient from the site. A soil sample collected
at Location BC-1, at a depth of 2.5 to 3 feet showed TCE
concentrations of 17,000 ug/!. and PCE concentrations of
13,000 ug/l. BC-1 is located near the door of the
manufacturing building where the Department's 1989 soil gas
samples were taken. As previously indicated, this location has
been identified by former Victor employees as an area where
hazardous substances were disposed

Groundwater samples showed TCE concentrations of

25 ug/! at Location HP-7 (downgradient) and non detect

Apdx B - 69

concentrations of TCE and PCE at Location HP-3
(upgradient) in the shallow unconfined aquifer These samples
confirm releases of hazardous substances at the site

224 During December 1989 Vic, Inc. hired a
consultant (Environmental Strategies Corporation) to install

four groundwater monitoring wells and collect samples of soll

and groundwater at the Site No detectable concentrations of

TCE or PCE were located upgradient, and low concentrations
of TCE (1 to 6 ug/l) were found downgradient from the
facility, in the upper portion of the shallow unconfined aquifer

Health Risks of Substances Found

>)

we

eat TCE and PCE are suspected human
carcinogens Exposure is by ingestion, inhalation, or direct
contact Both chemical act as a narcotic in high
concentrations. PCE can cause dermatitis with prolonged skin
contact. TCE in high concentrations may cause hepatocellular

carcinonoma ~The California drinking water maximum

Apdx B - 70

contaminant level (MCL) is 5 0 parts per billion (ppb) for both
PCE and TCE. A MCL is a water quality standard set by the
Department of Health Services. For carcinogens in drinking
water, it is based on a one-in-one-million cancer risk

2.4 Population at Risk Drinking water supplies have
been severely impacted by the disposal of TCE and PCE at the
former Victor Industries facility. This includes both municipal
and private drinking water supplies. Chico's water purveyor,
California Water Service Company (CWS) has been required
to collect water samples repeatedly from their deep wells both
upgradient and downgradient from the Victor Industries
facility. TCE has been detected in four municipal wells all
located downgradient from the Site. One of those wells
(CWS No. $1) contained concentrations of TCE at 2.5 ug/l
This well is located only four city blocks downgradient from
the Site. It is a high volume pumping well (+900 gallons per

minute) with a long screened intake interval. The state

Apdx B - 71

maximum contaminant level (mel) of TCE for drinking water
is 5.0 ug/l. These deep wells have "drawn" the TCE from the
Victor source downward into the deep aquifers that supply
groundwater to the CWS wells

During 1989 and 1991 the Department collected
samples from 190 private wells, all downgradient, from the
Site. A majority of these wells, 186, supply water to
residences, and four supply water to Louisiana Pacific
Corporation's (L-P) industrial facility. All four of the L-P
wells contained TCE, and concentrations exceeded 140 ug/l
in one of them. At the time these samples were collected, L-P
employees were drinking the water. L-P immediately began
supplying its. employees with bottled water, after the
Department notified L-P of its sampling results. The other
186 private wells are located in the Stanley Park subdivision,
outside the Chico City limits. Of the 186 wells tested, 62 of

them contained concentrations of TCE and/or PCE, 1,1,1

Apdx B - 72

aE SaSEY.

TCA, and DCE. Nine of these 62 impacted private wells
contain concentrations of TCE exceeding the MCL of 5.0
ug/l. The residential wells in Stanley Park are relatively
shallow -in depth (55 to 160 feet). The deepest wells owned
by L-P and those in Stanley Park contain the highest
concentrations of TCE. This is indicative that the contaminant
plume in, the groundwater has traveled a long distance. The
Stanley Park subdivision contains the "leading edge" of the
plume, and is the furthest distance from the Victor Site
(approximately one mile).

2.5 Routes of Exposure The principal exposure route
is through the drinking water supply. The water supply
system for the main City of Chico is interconnected and any
one contaminated well can affect the entire water supply. This
puts the 100,000 residents of Chico at risk if contaminated
water at significant concentrations enters the water supply

The residents in the Stanley Park subdivision are at a much

Apdx B - 73

greater risk, due to the fact that they are solely dependent on
their private wells for drinking water In addition, the TCE
plume will spread to other water supply wells, which will
likely include the Chico Mobile Country Club. This mobile
home park with 180 residential hookups is directly
downgradient from the plume and is one block south of the
Stanley Park subdivision

A second exposure route is through direct contact with
inhalation of TCE and PCE vapors. Inhalation occurs by the
volatization of TCE from contaminated water in a shower or
laundry area. According to a study performed at the
Lawrence Livermore Laboratory the inhalation exposure
pathway from contaminated water is at least equal in risk to
that of ingestion

3.0 Conclusions of Law

3.0.1 Victor Industnes, Vic. Inc.. Charles A. Tackman

and Albert F. Campbell as Trustees on behalf of the Victor

Apdx B - 74

ht det ah a ay

vai fb ec ba a ie edad cnn

Muscat Trust, CCL Industries and Advanced Monobloc, Inc
are responsible parties or "liable persons," as defined by
H&SC Sections 25319, 25323.5 and 25385. 1(g)

3.02 TCE and PCE are “hazardous substances," as
defined by H& SC Section 25316, and have been found at the
site

303 A “release” or threatened release of the
hazardous substances TCE and PCE has occurred at or from
the site, as defined by H& SC Section 25320

304 The actual and/or threatened release of
hazardous substances at the site may present an imminent and
substantial endangerment to the public health or welfare or to
the environment

lll QRDER

40 Based on the foregoing FINDINGS AND

CONCLUSIONS OF LAW, the Department hereby

determines that removal and remedial action is necessary on

Apdx B - 75

and off the site because there may be an imminent and
substantial endangerment to the public health or welfare or to
the environment. IT IS HEREBY ORDERED THAT the
Responsible Parties conduct the following response activities
in the manner specified herein, and in accordance with a
schedule specified by the Department as follows.

41 ALL WORK PERFORMED UNDER THIS
ORDER SHALL BE CONSISTENT WITH AND BASED
ON the Comprehensive Environmental Response, and
Compensation and Liability Act (CERCLA) (42 U.S.C. 9601
et sea., as amended, the National Contingency Plan (40 Code
of Federal Regulations (CFR) Part 300), as amended, state
laws and regulations, and other current and applicable U.S.
Environmental Protection Agency (EPA) and Department
guidelines and standards.

4.2 Notification of Intent to Comply. Within 15

calendar days of the effective date of this order, the

Apdx B - 76

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2
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Responsible Parties shall submit a written notice of their intent
to comply with the terms of this Order
4.3 Removal Actions. The Responsible Parties shall
implement the following removal actions after workplans and
time schedules for such removals have been approved by the
Department. The Respondents shall keep the community
informed of removal actions by submitting and distributing
fact sheets, after they have been approved by the Department
Workplans and time schedules for implementing the removal
actions shall be submitted by the specific dates ‘used below
A Drinking Waterline Construction. A drinking
waterline extension and all necessary
distribution lines shall be constructed in the
Stanley Park Subdivision. This distribution
system for public water supplies shall include
hooking up all private wells containing

concentrations of TCE, PCE, and/or 1.1.1

Apdx B - 77

TCA, and DCE that exceed their MCL as
identified in previous Department well
sampling events. In addition, to protect the
residents with wells containing concentra_ions
of contaminants that do not exceed their
MCL's, a choice of the following two
alternatives shall be made: 1) Quarterly
samples shall be taken of all these private
wells, or 2) All these private residences shall
be hooked up to the new waterline. These
actions are necessary because as the plume
advances, contaminant concentrations may rise
and additional private wells may be impacted.
Locations of these private wells shall include,
but not be limited to those wells located on
Orchard, Diamond, Marian and Stanley

Avenues, and Dayton Road, Harper Valley and

Apdx B - 78

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Shawna Lanes, Barrington and Solar Estates
Drives, and Serenity Way. A workplan to
implement this construction shall be submitted
to the Department for review and approval
within 40 days of the date of issuance of this
order. Construction of the waterline shall be
completed within 120 days of issuance of this
Order.

Groundwater Extraction and Treatment

Responsible Parties shall submit a workplan to
the Department for review and approval
discussing different treatment technologies,
and engineering and cost analysis to extract
and treat contaminated groundwater onsite
and/or offsite, based upon a request from the
Department at a later date. A design and

implementation schedule shall be submitted to

Apdx B - 79

the Department for review and approval of the
recommended treatment and extraction system
within 120 days of the Department's approval
of the engineering and cost analysis.

Groundwater Extraction and Treatment

Evaluation Report. After four (4) months of
operation of the extraction system, an
evaluation report shall be prepared and
subinitted to the Department for review and
approval. This report shall evaluate the
effectiveness and capture zone of the
extraction system for the removal of organic
solvent constituents from groundwater. The
Responsible Parties shall submit any additional
reports for Department review and approval as
required by the Department.

Responsible Parties shall undertake additional

Apdx B - 80

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Removal Actions if the Department determines
that they are necessary for the protection of
the public health or welfare or the
environment. Upon request by the
Department, Responsible Parties shall submit
Removal Action workplan and schedule for
approval by the Department. Responsible
Parties shall implement the Removal Action
workplan as approved by the Department in
accordance with the approved schedule.

44 Groundwater Monitoring. The Responsible
Parties shall immediately begin interim groundwater
monitoring at onsite, off site and Stanley Park wells in
accordance with previous site groundwater monitoring plans
approved by the Department. Groundwater level
measurements shall be conducted quarterly commencing the

first month after the date of issuance of this order.

Apdx B - 81

Groundwater sampling shall also be conducted on a quarterly
basis commencing in the same month as above. Subsequent
monitoring shall be conducted until the Department

determines it 1s appropriate to terminate monitoring

ial Investi

A RI/FS shall be conducted for the Site. The RI/FS shall be
prepared consistent with the U.S. Environmental Protection
Agency's "Guidance for Conducting Remedial Investigations
and Feasibility, Studies under CERCLA", October 1988 and
the National Contingency Plan (40 Code of Federal
Regulations (CFR) Part 300), as amended, state laws and
regulations, and other current and applicable US.
Environmental Protection Agency (EPA) and Department
guidelines and standards. The purpose of the RI/FS is to
assess site conditions and evaluate alternatives to the extent
necessary to select a remedy. RI and FS activities shall be

conducted concurrently and iteratively so that the

Apdx B - 82

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investigations can be completed expeditiously. The following
elements of the RI/FS process and those defined by the
Department in Section 4.1 of this Order shall be preliminarily
defined in the initial site scoping and refined and modified as

additional information is gathered throughout the RI/FS

process
A Remedial Action objectives including
applicable or relevant and appropriate
requirements (ARARs)
B Project phasing including the identification of

removal actions and operable units

4.5.1 RVFS Workplan. Within 60 days of the effective

date of this Order, Responsible Parties shall prepare and
submit to the Department for review and approval, a detailed
RI/FS Workplan and implementation schedule which covers
all the activities necessary to conduct a complete remedial

investigation and feasibility study of the Site and any offsite

Apdx B - 83

areas where there is a release or threatened release of
hazardous substances from the Site. The RI/FS Workplan
shall include a detailed description of the tasks to be
performed, information or data needed for each task, and the
deliverables which will be submitted to the Department.
These 13 deliverables are discussed in the remainder of this
Section, with a schedule for implementation, and monthly
reports. Because of the unknown nature of the Site and the
iterative nature of the RI/FS, additional data requirements and
analysis may be identified throughout the process. Either the
Responsible Party or the Department may identify the need for
additional work. The RI/FS Workplan shall include all the
elements listed below
A Project Management Plan <A_ Project
Management Plan which describes how the
project will be managed by Responsible Parties

and its contractors, subcontractors, and

Apdx B - 84

consultants including an organization chart
with the names and titles of key personnel and
a description of, their individual
responsibilities

Scoping Document. The scoping document

shall be developed in consideration of the
program goal, program management
principles, and expectations contained in the
NCP. It shall include
An Analysis and summary of the site
background and the physical setting
At a minimum, the following
information is required
(a) A map of the site, description
of past and current
manufacturing processes if

they exist, aerial photographs

Apdx B - 85

(b)

(C)

and blue prints showing
buildings and structures;

A description of past disposal
practices,

A list of all hazardous
substances, materials or wastes
which were disposed,
discharged, spilled, treated,
stored, transferred,
transported, handled or used at
the Site, and a description of
their estimated volumes,
concentrations, and
characteristics;

Since lead was used in the
production of metal tubes at

the Site, it shall be explored

Apdx B - 86

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and analyzed as a target
hazardous waste around the
manufacturing facility, and
(e) A description of hazardous
substance characteristics
A summary of all contaminant investigations
shall be made identifying the horizontal and
vertical extent of contamination in soil, soil
gas, and groundwater. Spatial and temporal
trends shall be evaluated. Responsible Parties
shall create maps showing concentration lines
of contaminants in soils, soil gas, and

groundwater.

One of the objectives of the RI shall be to determine

the nature and full extent of hazardous substance

contamination in the soil-and groundwater at the site

and from the site including off-size areas affected by

Apdx B - 87

releases from the site. This shall be accomplished by

collecting soil samples and installing groundwater

monitoring wells in the following locations

Three (3) clusters of three (3) monitoring
wells each shall be installed along Park
Avenue, within the boundary of the TCE
plume, downgradient from the site. One (1) of
the clusters shall be installed in the City right-
of-way near the PG&E Substation, one (1)
cluster of wells shall be installed near Park
Avenue and 20th Street, and one (1) cluster of
wells shall be installed two blocks further
north along Park Avenue. Each of these three
(3) well clusters shall have screens constructed
in each of three (3) separate groundwater
aquifers as follows: one well each shall be

completed in the shallow unconfined zone

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(approximately 20-40 feet below ground
surface), one well each in the upper confined
zone (approximately 90-120 feet below
ground surface), and one well each in the
lower confined zone (approximately 150-170
feet below ground surface).

Three (3) clusters of three (3) monitoring
wells each shall be installed between Park
Avenue and the Louisiana-Pacific facility,
downgradient from the site. One of the
clusters shall be installed along 21st Street
Another cluster shall be installed along 19th
Street and the third shall be installed along
17th Street, all between Broadway and Salem
Streets. Each of the three (3) well clusters
shall have screens constructed in each of the

three (3) separate groundwater aquifers as

Apdx B - 89

follows: one well each shall be completed in
the shallow unconfined zone, one well each
shall be completed in the upper confined zone,
and one well each shall be completed in the
lower confined zone

Two (2) additional well clusters of three (3)
monitoring ‘ells each shall be installed in the
Stanley Park Subdivision, downgradient from
the site. Gne of the well clusters shall be
installed in the almond orchard, next to the
furthest house north an Diamond Avenue. The
other well cluster shall be installed near the
intersection of Stanley Avenue and Dayton
Road, at the leading edge of the plume. Each
of the two (2) well clusters shall have screens
constructed in each of the three (3) separate

groundwater aquifers, such as those denoted in

Apdx B - 90

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item Cl and 2.

All wells installed as part of the Remedial
Investigation shall be constructed in
accordance with the Department's technical-
standards for groundwater monitoring well
construction. The Department shall have final
approval authority over all well construction
specifications and all wells shall meet the
Department's minimum technical standards.
The Department may require that the geology
of each location be characterized by
continuous coring of pilot boreholes prior to
construction of monitoring wells, and, the pilot
boreholes required by the Department shall be
geophysically logged.

Determine the magnitude and probability of

actual or potential harm to public health, safety

Apdx B - 9]

6

or welfare or to the environment posed by the
threatened or actual release of hazardous
substance from the site. This shall include, but
not be limited to the collection and analysis of
water samples taken from municipa! and
private drinking water wells in the plume
Identify and evaluate appropriate response
measures to prevent or minimize future
releases and mitigate any releases which have
already occurred

Collect and evaluate the information necessary
to prepare a Remedial Action Plan (RAP) in
accordance with the requirements of Health &
Safety Code Section 25356 |

The RI workplan shall also include provisions
for quarterly monitoring of all groundwater

monitoring wells installed by the Responsible

Apdx B - 92

Parties. At a minimum, the samples shall be
analyzed for the following purgeable
halocarbons:

fe) Trichloroethylene (TCE)

O Perchloroethylene (PCE)

fo) 1,1, Dichloroethylene (DCE)

O Trans 1,2 Dichloroethylene

O Cis 1,2 Dichoroethylene

The Department also reserves the right to
require the Responsible Parties to analyze for
any additional substances as warranted.

The RI workplan shall include measures to
evaluate the impact of water level changes an
plume migration and direction These
provisions shall include at a minimum monthly
measurements of water level elevations.

Responsible Parties shall provide a monthly

Apdx B - 93

report providing water elevations and contour
maps for each aquifer

9 Collect soil samples on the Site to determine
the extent of contamination from toxic metals

including lead.

D. Field Sampling Plan. The field sampling plan shall

include:

I. Sampling objectives

2. Sample location and frequency

3. Sample designation or numbering system

4 Detailed specification of sampling equipment
and procedures

. Sample handling and analysis including
preservation methods, shipping requirements
and holding times

6. Management plan for wastes generated

E Quality Assurance Project Plan. The plan shall

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Project organization and responsibilities.
Quality assurance objectives for measurement
including accuracy, precision, and method
detection limits. Selection of analytical
methods shall consider obtaining detection
limits at or below health detection levels for
environmental media.

Sampling procedures

Sample custody procedures and
documentation.

Field and laboratory calibration procedures.
analytical procedures.

Laboratory to be used certified pursuant to
Health and Safety code Section 25198.
Procedures used to assess data (precision,

accuracy and completeness) and corrective

Apdx B - 95

actions.
9 Reporting procedure for measurement system
performance and data quality.
Health and Safety Plan. The Health and Safety Plan
shall include the following as a revised resubmittal for
the next phase of activities:
The name of a site health and safety officer
and the names of key personnel and alternates

responsible for site safety and health

to

A health and safety risk analysis for existing
site conditions, and for each site task and

operation

we

Employee training assignments.

4 A description of personal protective equipment
to be used by employees for each of the site
tasks and operations being conducted

5 Medical surveillance requirements

Apdx B - 96

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A description of the frequency and types of air
monitoring, personnel monitoring, and
environmental sampling techniques and
instrumentation to be used.

Site control measures.

Decontamination procedures.

Standard operating procedures for the site.

A contingency plan that meets the
requirements of 29 CFR 1910.12 0 (1) (1) and
(1) (2).

Entry procedures for confined spaces.

Schedule. A schedule which provides specific time

frames and dates for completion of each activity and

report conducted or submitted under the RI/FS

Workplan including submittal of the Remedial

Investigation Report, Baseline Risk Assessment and

Feasibility Study Report in compliance’ with

Apdx B - 97

paragraphs 4.7, 4.8, and 4.9 of this Order

4.5 RI/ES Workplan Implementation. Responsible Parties

shall implement the RI/FS Workplan as approved by the
Department in accordance with the approved schedule

4.6 Public Participation Plan (Community Relations). The

Responsible Parties shall prepare and submit within 120 days
for Department review and approval, a Public Participation
Plan (PPP) which describes how, under the Order, the public
and the adjoining community will be kept informed of
activities conducted at the Site and how the Responsible
Parties will be responding to inquiries from concerned citizens.
The PPP must be developed in accordance with the H&SC
Section 25356.1 et. seq. , and the Department's Public
Participation Policy and Guidance Manual.

4.7 Remedial Investigation (RI) Report. The RI
Report shall be prepared and submitted by Responsible Parties

to the Department for review and approval in accordance with

Apdx B - 98

the approved RI/FS Workplan schedule. The purpose of the
RI is to collect data necessary to adequately characterize the
site for the purposes of defining risks to public health and the
environment and developing and evaluating effective remedial
alternatives. Site characterization may be conducted in one or
more phases to focus sampling efforts and increase the
efficiency of the investigation. The Responsible Parties shall
identify the sources of contamination and define the nature,
extent, and volume of the contamination. Using this
information the contaminant fate and transport shall be
evaluated. The RI Report shall contain
A Site Physical Characteristics. Data on the
physical characteristics of the site and
surrounding area should be collected to the
extent necessary to define potential transport
pathways and receptor populations and to

provide sufficient engineering data for

Apdx B - 99

development and screening of remedial action

alternatives. The data shall include

Current and historical surface features
including facility dimensions and
locations (buildings. tanks, piping,
etc.), surface disposal areas, fencing,
property lines and _ utility _ lines,
roadways and railways, drainage
ditches, leached springs, surface water
bodies, vegetation, topography.
residences, and commercial buildings
The data may include historical
photographs, past topographic
surveys, operational records, and
information obtained from interviews
with owners, operators, local

residents, and local regulatory

Apdx B - 100

to

agencies

Regional and site geology including
the location and characteristics of
surface Be: bodies, stratigraphic
geologic cross-sections and fence
diagrams, description of drainage
patterns, surface water/groundwater
relationships and water quality.
Characteristics and chemistries of
surface soils and vadose zone.

Surface water hydrology including the
location and characteristics of surface
water bodies, description of drainage
patterns, surface water/groundwater
relationship and water quality.

Site hydrogeology including

groundwater occurrence, movement,

_Apdx B - 101

recharge/discharge and quality and
aquifer characteristics
6 Meteorology as reiated to atmospheric

transport and health and safety .

~

Human populations and land use of
people potentially exposed
8 Ecological information including
ecosystem components and
characteristics, critical habitats, and
biocontamination
B Sources of Contamination Contamination
sources (including heavily contaminated
media) shall be defined. The data shall include
the source locations, type of containment.
waste characteristics, and site features related
to contaminant migration and human exposure

C. # Nature and Ex f Contaminati

Apdx B - 102

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Contaminants shall be identified and the
horizontal and vertical extent of contamination
shall be defined in soil, groundwater, surface
water, air. biota and facilities. Spatial and
temporal trends. shall be _ evaluated
Responsible Parties shall create maps showing
iso-concentration lines of contaminants in
soils, soil gas, and groundwater in each
aquifer

Recommendations for additional Remedial

Investigations. The RI Report shall include
recommendations for additional remedial
investigations to fully characterize the lateral
and vertical extent of contamination in the soil
and groundwater. A new RI sampling plan
shall be submitted and a new workplan and

schedule provided pursuant to paragraph 4.5

Apdx B - 103

48 Baseline Risk Assessment. The responsible
parties shall submit a Baseline Risk Assessment Report for
Department review and approval within 120 days from the
submittal of the RI report. The Report shall be prepared
consistent with EPA guidance: Risk Guidance for Superfund,
Volume |, Human Health Evaluation Manual, December
1989, and Risk Assessment Guidance for Superfund, Volume
2, Environmental Evaluation Manual, March 1989. The
Baseline Risk Assessment Report shall include the following
components

A. Contaminant Identification. Screen

characterization data to identify contaminants
of concern and, if useful, "indicator chemicals"
as discussed in EPA RI/FS guidance

B. Environmental Evaluation. An ecological

assessment consisting of.

l Identification of sensitive environments

Apdx B - 104

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and rare, threatened, or endangered

species and their habitats

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As appropriate, ecological
investigations to assess the actual or
potential effects an the environment
and/or develop remediation criteria.
Exposure Assessment. The objectives of an
exposure assessment are to identify actual or
potential exposure pathways to characterize
the potentially exposed populations, and to
determine the extent of the exposure
Toxicity Assessment. Evaluate the types of
adverse health or environmental effects
associated with and multiple chemical
exposures, the relationship between magnitude
of exposures and adverse effects, and related

uncertainties such as the weight of evidence

Apdx B - 105

for a chemical's potential carcinozenicity in

humans
E Risk Characterization. Characterization of the
potential risks of adverse health or
environmental effects for each of the exposure
scenarios derived in the exposure assessment
49 Feasibility Study Report. The Feasibility
Study (FS) Report shall be prepared and submitted by
Responsible Parties to the Department for review and
approval, in accordance with the approved RI/FS Workplan
schedule. The FS Report shall summarize the results of the RI

including the following

A Documentation of all treatability studies
conducted
B Development of medium specific or operable

unit specific remedial action objectives

including ARARs

Apdx B - 106

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Identification and screening of general
response actions, remedial technologies, and
process options on a medium and/or operable
unit specific basis

Evaluation of alternatives based on the criterta
contained in the NCP and H&SC Section
25356.1 including

| Overall protection of human health and

the environment

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Compliance with ARARs

iP)

Long term effectiveness and
performance
4 Reduction of toxicity, mobility, or

volume through treatment

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Short term effectiveness
6 Implementability based administrative

feasibility

Apdx B - 107

z; Cost
8. State and local agency acceptance
9. Community acceptance

E Proposed remedial actions.

4.10 Remedial Action Plan. No later than 45 days

after Department approval of the FS Report, Responsible
Parties shall prepare and submit to the Department for review
and approval, a draft Remedial Action Plan (RAP). The draft
RAP shall be consistent with the NCP and H&SC Section
25356.1 et seq. The draft RAP will be based on the approved

RI/FS Reports, and shall concisely and clearly set forth:

A Health and safety risks posed by the conditions
at the site.
B. The effect of contamination or pollution levels

upon present, future, and probable beneficial
uses of contaminated, polluted, or threatened

resources.

Apdx B - 108

D

The effect of alternative remedial action
measures on the reasonable availability of
groundwater resources for present, future, and
probable beneficial uses

Site specific characteristics, including the
potential for offsite migration of hazardous
substances, the surface or subsurface soil, and
the hydrogeologic conditions, as well as pre-
existing background contamination levels
Cost effectiveness of alternative remedial
action measures. Land disposal shali not be
deemed the most cost-effective measure
merely on the basis of lower short-term cost
The potential environmental impacts of
alternative remedial action measures,
including, but not limited to, land disposal of

the untreated hazardous substances as opposed

Apdx B - 109

to treatment of the hazardous substances to

remove or reduce its volume, toxicity, or

mobility prior to disposal.

G. A statement of reasons setting forth the basis
for the removal and remedial actions selected.
The statement shall include an evaluation of
each propused alternative submitted and
evaluate the consistency of the removal and
remedial actions proposed by the plan with the
federal regulations and factors specified in
subdivision (c) of H& SC Section 25356. 1.

H A schedule for implementation of all proposed
remedial actions
In conjunction with the Department, the
Responsible Parties shall implement the public
review process specified in H&SC Section

25356. 1(d)(1) et seq

Apdx B - 110

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Following the Department's review of the
input obtained from the public review process,
the Department will specify to the Responsible
Parties changes to be made in the RAP. The
Responsible Parties shall modify the document
in accordance with the Department's
specification and submit a final RAP within 15
days of Department's comments.

4.11 Preparation of Remedial Action Workplan and

Design (RAWD). Within 90 days after Department approval

of the final RAP, in accordance with H&SC Section 25356.1,
Responsible Parties shall submit to the Department for review
and approval a detailed RAWD describing the implementation
of the final RAP containing the following elements:
A. Design criteria and final plans and
specifications for facilities to be constructed

B. Description of equipment to be used to

Apdx B - 111

G

excavate, handle, and transport contaminated
material

A field sampling plan addressing sampling
during implementation and to confirm
achievement of the performance objectives of
the RAP

A transportation plan identifying routes of
travel and final destination of wastes generated
and disposed (if applicable).

An updated health and safety plan addressing
the implementation activities.

Identification of any necessary permits and
agreements.

An operation

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Source: Frix Law Library, https://www.frixlaw.com/law-library/documents/brief%3Amicro_IA40386006_1683%3A1. Public record. Not legal advice.
