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ADVANCED MICRO DEVICES v. NATIONAL SEMICONDUCTOR

United States District Court, Northern District of California


February 12, 1999

ADVANCED MICRO DEVICES, INC., PLAINTIFF,
v.
NATIONAL SEMICONDUCTOR CORPORATION AND UNITED TECHNOLOGIES CORPORATION, DEFENDANTS. AND RELATED ACTIONS

The opinion of the court was delivered by: Whyte, District Judge.

   

           ORDER GRANTING IN PART AND DENYING IN PART DEFENDANTS'
                    MOTION FOR PARTIAL SUMMARY JUDGMENT

Defendant and counter-claimant National Semiconductor and defendant United Technologies Corporation's ("defendants") motion for partial summary judgment was heard on January 29, 1999. The court has read the moving and responding papers and heard the argument of counsel. For the reasons set forth below, the court grants the motion in part and denies it in part. Summary judgment is granted as to the fourth, fifth, seventh, eighth and eleventh causes of action. Summary judgment is denied as to the first and third causes of action.

I. BACKGROUND

In 1982, plaintiff Advanced Micro Devices, Inc ("AMD") initiated subsurface investigations at its manufacturing facility at 1165 Arques Avenue, Sunnyvale, California (the "Site") as a result of suspicions of leakage from underground chemical solvent storage tanks and from chemical handling and storage areas.*fn1 Declaration of Malinda Allison in Support of Defendants' Motion for Partial Summary Judgment ("Allison Decl."), Ex. A at 4. That year, a number of monitoring wells were drilled, and tests detected volatile organic compounds, principally in the ground water of the A and B aquifers under the Site. Id. at 4-6. After two phases of investigation at the Site were completed, the California Regional Water Quality Control Board ("RWQCB") requested that AMD begin studies for the installation and operation of a ground water extraction and treatment system, and Phase 3 studies were developed to comply with the RWQCB's request.*fn2 Id. at 7.

In 1984, AMD removed two subsurface waste solvent tanks and two subsurface acid neutralization systems. Id. 7, Ex. A at 13, 14, 41.

In 1986, AMD "initiated an interim remedial measure in the `A' aquifer," consisting of the installation of ground water extraction wells, with the investigation continuing. Id. at ES-4, 8. Several of the borings that had been drilled into the aquifers were converted to monitoring wells, and several borings and monitoring wells were converted to extraction wells. Id. at 8-9. On August 20, 1986, the RWQCB issued Order No. 86-64, Waste Discharge Requirements, in which it reported:

  [f]urther investigation and interim remedial
  action are necessary to prevent the
  continued migration of pollutants to
  unaffected groundwaters and to preclude
  loss of existing and potential beneficial
  uses of said waters. The board
  intends to establish final cleanup objectives

  for the site after review of the
  results of actions required by this order.

Declaration of Reed M. Content in Opposition to Motion of Defendants for Partial Summary Judgment, ("Content Decl.") Ex. 2 at 2 ! 6. The extraction wells were connected to a centrally located ground water treatment facility, which began full-time operation in 1986. Declaration of Lance D. "Geselbracht in Support of Defendants' Motion for Partial Summary Judgment ("Geselbracht Decl.") Ex. B. ! 2.3. By 1987, the EPA had placed the Site on the National Priority List for cleanup. Allison Decl. at Table 1.

On June 15, 1987, in response to the RWQCB's Waste Discharge Requirements, AMD submitted a Ground Water Extraction System Installation report to the RWQCB. Geselbracht Decl.Ex. A. The report stated in part that "all ground water extraction efforts have been directed to the `A' level aquifer," that ground water extraction and treatment systems were operational, and that the eight A aquifer extraction wells should be operational "until the final zone of influence can be determined," at which point "additional extraction wells may be required." Id. at !! 1.1, 5.1.1-5.2.1.

On August 15, 1987, a Ground Water Extraction and Treatment System Status Report prepared for AMD reported that AMD was not responsible for contamination in the B aquifer, but that additional extraction wells may be required "in order to establish the necessary hydraulic control to contain and cleanup the MMU plume "in the A aquifer. Id. Ex. B at !! 4.2, 2.2. The report stated that "[t]he treatment facility has proved to be effective in removing volatile chemicals from ground water." Id. at ! 2.3. AMD initiated B aquifer extraction activities in 1988 as an "interim remedial measure." Allison Decl. Ex. A at 9.

On April 19, 1989, Administrative Order No. 89-061 adopted the cleanup site requirements for AMD. Id. Ex. A at 1.

In April, 1991, AMD's Final Draft Remedial Investigation ("RI") was prepared in response to the 1989 Administrative Order. Id. Ex. A. The RI stated that:

  [t]he purpose of this RI is to define the
  nature and extent of contaminants in the
  environment . . . to characterize the hydrogeological
  conditions to the extent
  necessary for the development, selection,
  and design of appropriate remedial
  actions; and to assess the risk to human
  health and the environment . . . These
  results will be used in the FS portion of
  the RI/FS [Draft Remedial
  Investigation/Feasibility Study] to determine
  remedial action alternatives and additional
  remedial action(s) necessary and appropriate
  for the Site.

Id. at 1-2. The RI noted that the existing "interim remediation program consists of pumping and treatment of ground water from several `A' aquifer extraction wells installed in August 1986," and that "the data collected as part of this RI are sufficient to complete the assessment of final remedial measures for the soil and ground water cleanup." Id. at ES-5. AMD submitted a final draft FS (Feasibility Study) Report on May 9, 1991. Allison Decl.Ex. B at 5.

On September 20, 1991, the RWQCB adopted California RWQCB Board San Francisco Bay Region Order No. 91-139, Site Cleanup for Advanced Micro Devices, National Semiconductor Corporation. Id. Ex. B. The September 20, 1991 order in part reviewed AMD's RI/FS and stated that the technical information in the RI and FS Reports "is acceptable for developing a final cleanup plan" and that the reports "contain an evaluation of applicable or relevant and appropriate requirements . . . the interim remedial actions, final remedial alternatives, and proposed remedial standards." Id. Ex. B at 5. The order also stated that AMD would be held "jointly responsible for ground water cleanup in the A and B aquifers" pursuant to the RWQCB cleanup order. Id. The order reviewed the "interim remedial actions" which AMD had implemented in 1986, consisting of the extraction and treatment of the A aquifer water from wells and the addition of three extraction wells in 1988. Id. at 9. The order evaluated the alternatives which had been set out in AMD's Feasibility Study, and provided a summary of the "final remedy for Subunit 2" based primarily on the information provided in the RI/FS Reports.*fn3 Id. at 12.

In September of 1991, the EPA issued its Record of Decision ("ROD"), which presented the "selected remedial action" for the Site. Content Decl.Ex. 1 at 6. The ROD described the current, ongoing ground water extraction activities, which were "implemented under RWQCB authority with the goal of controlling further contaminant migration while ongoing site investigations continued to collect the data necessary for final remedial action." Content Decl.Ex. 1 at 20. The ROD then presented the elements of the "selected final remedy" and the steps necessary to implement that remedy. Id. at 6-7, 20-22. The ROD reported that "the currently operating extraction system will be expanded" in order to implement the final remedy. Id. at 20. The ROD stated that

  [t]he goal of this remedial action is to
  restore the groundwater to its beneficial
  use, which is, at this site, a potential
  source of drinking water. Based on information
  obtained during the RI and on
  a careful analysis of all remedial alternatives,
  EPA and the RWQCB believe that
  the selected remedy will achieve this
  goal.

Id. at 46.

AMD filed the present contribution action on September 19, 1997.

II. ANALYSIS

A. AMD's First and Third Causes of Action Under CERCLA

1. Actions for Contribution under CERCLA

Section 107(a) of CERCLA, 42 U.S.C. § 9607 (a), authorizes actions against statutorily defined "responsible parties" to recover a party's costs incurred in cleaning up hazardous waste disposal sites. Pinal Creek Group v. Newmont Mining Corp., 118 F.3d 1298, 1300 (9th Cir. 1997). 42 U.S.C. § 9613 (g)(2) provides the statute of limitations for such cost recovery actions:

(2) Actions for recovery of costs

    An initial action for the recovery of
  the costs referred to in section 9607 of
  this title must be commenced —

    (A) for a removal action, within 3
  years after completion of the removal
  action, except that such cost recovery
  action must be brought within 6 years
  after a determination to grant a waiver
  under section 9604(c)(1)(C) of this title
  for continued response action; and

    (B) for a remedial action, within 6
  years after initiation of physical on-site
  construction of the remedial action, except
  that, if the remedial action is initiated
  within 3 years after the completion
  of the removal action, costs incurred in
  the removal action may be recovered in
  the cost recovery action brought under
  this subparagraph . . .

In 1986, Congress amended the CERCLA statute to clarify and confirm that, in addition to allowing cost recovery actions by non-responsible parties against responsible parties, CERCLA also recognizes claims for contribution between "potentially liable parties." The new statute, 42 U.S.C. § 9613 (f)(1), specifically provides:

  (1) Contribution. Any person may seek
  contribution from any other person who
  is liable or potentially liable under section
  9607(a) of this title, during or following
  any civil action under section
  9606 of this title or under 9607(a) of this
  title. Such claims shall be brought in
  accordance with this section and the

  Federal Rules of Civil Procedure, and
  shall be governed by Federal law. In
  resolving contribution claims, the court
  may allocate response costs among liable
  parties using such equitable factors as
  the court determines are appropriate.
  Nothing in this subsection shall diminish
  the right of any person to bring an
  action for contribution in the absence of
  a civil action under section 9606 of this
  title or section 9607 of this title.

42 U.S.C. § 9613 (g)(3) was also added to provide the statute of limitations for § 113(F)(1) contribution actions:

  (3) Contribution. No action for contribution
  for any response costs or damages
  may be commenced more that 3 years
  after —

  (A) the date of judgment on any action
  under this chapter for recovery of
  such costs or damages, or

  (B) the date of an administrative order
  under section 9622(g) of this title
  (relating to de minimis settlements) or
  9622(h) of this title (relating to cost recovery
  settlements) or entry of a judicially
  approved settlement with respect
  to such costs or damages.

As is discussed in Part II.A.2 below, § 113(g)(3) by its terms does not contemplate an "initial action," such as the present one, in which no action preceded the contribution suit and therefore no cost recovery judgment, order, consent decree or settlement can or will trigger the § 113(g)(3) limitation period.*fn4 The first question raised by the present motion is, therefore, what statute of limitations governs a § 113(f)(1) "initial action" for contribution.

                  2. The Applicable Statute of Limitations
                     for "Initial" Contribution Actions
                                Under CERCLA

In the absence of a statute of limitations expressly applying to "initial" contribution actions, defendants assert that the statute of limitations of 42 U.S.C. § 9613 (g)(2)(A), regarding recovery of costs for a "removal action," and (B), regarding recovery of costs for a "remedial action," govern this action. AMD, on the other hand, contends that § 113(g)(3) is the sole statute of limitations for contribution claims, and must be applied even where there can be no triggering event.

In Sun Co. Inc. v. Browning-Ferris, Inc., 124 F.3d 1187 (10th Cir. 1997), the plaintiffs brought a contribution action under § 113 after incurring cleanup costs in response to an EPA unilateral administrative order, which is not one of the triggering events under § 113(g)(3). The court recognized that potentially responsible parties ("PRP's") who were jointly responsible for a waste site could seek contribution from other PRP's, but that "[i]f those PRP's have never been defendants in a civil action under §§ 106 or 107, however, it appears that there is no statute of limitations governing their contribution claims." Sun, 124 F.3d at 1191. Therefore, plaintiffs who incur cleanup costs without a prior civil action "potentially have an unlimited time in which to bring their contribution claims." Id. The court in Sun addressed the problem by applying the limitations period of § 113(g)(2) to the contribution claim before it. That section applies, the court reasoned, because a § 113(g) contribution action is actually "an action for recovery of the costs referred to in § 107" from PRP's whose liability is defined by § 107. Id. at 1192. Defendants here argue that, under Suns, CERCLA §§ 113(g)(2)(A) and (B) are the statutes of limitations which apply to AMD's CERCLA contribution claims.

In Reichhold Chemicals, Inc. v. Textron, Inc., 888 F. Supp. 1116 (ND.Fla. 1995), however, the court held that § 113(g)(3) is the only statute of limitations applicable to a CERCLA contribution claim, even where there is no event to trigger the limitations period, and "[i]t is not necessary, or even proper, to borrow another limitations period." Reichhold 888 F. Supp. at 1125. In Gould, Inc. v. A & M Battery and Tire Service, 901 F. Supp. 906 (E.D.Pa. 1995), the plaintiff argued that, since none of the triggering events under § 113(g)(3) had occurred in his contribution action, the action could not be time-barred by that section. The court agreed, and held that the action was timely. Gould, 901 F. Supp. at 914-15.

The Ninth Circuit has yet to rule on the question of what statute of limitations applies in "initial" CERCLA contribution actions.*fn5 In City of Merced v. R.A. Fields, 997 F. Supp. 1326 (E.D.Cal. 1998), the court stated, in dicta, that either the Tenth Circuit's approach in Sun, or the approach applied by the Sun district court, whereby the § 113(g)(3) limitations period is triggered by an event not listed in the statute,*fn6 should apply. The court stated that it would not be inclined apply § 113(g) to an initial action, in which the statute could never be triggered. City of Merced, 997 F. Supp. at 1334.

The court agrees with the Eastern District's indication in City of Merced that some limitations period which is capable of accrual should apply to an initial contribution action, and adopts the approach taken by the Tenth Circuit in Sun. A contribution action is a type of cost recovery action, and, prior to the enactment of § 113(f), courts recognized an implicit right to contribution arising out of § 107 cost recovery actions. See U.S. v. Colorado & Eastern R. Co., 50 F.3d 1530, 1535 (citing Mardan Corp. v. CGC Music Ltd., 804 F.2d 1454, 1457 n. 3 (9th Cir. 1986) ("district courts have interpreted § 107 of CERCLA to impose, as a matter of federal law, joint and several liability for indivisible injuries with a correlative right of contribution.")). Accordingly, where the plaintiff in Pinal Creek argued that the § 113(g)(2) cost recovery statute of limitations could not apply to its contribution action, the Ninth Circuit, without ruling on the question, responded that the argument was

  based on the incorrect premise that a
  contribution action is not brought under
  § 107. Thus, the choice presented between
  a contribution action created and
  governed exclusively by § 113, on the
  one hand, and an independent "cost recovery
  action" available to working
  PRPs exclusively under § 107, on the
  other, is a false one. As we have concluded
  above, a PRP's contribution action
  finds implicit recognition in § 107;
  § 113 merely regulates its implementation.

Pinal Creek, 118 F.3d at 1305 n. 7. Therefore, the court concludes that § 113(g)(2) applies to initial contribution actions under CERCLA, since § 113(g)(2) expressly provides the statute of limitations for § 107, the original source of the right to contribution under CERCLA.

             3. The § 113(g)(2)(A) Limitations Period for
                        "Removal Action" Cost Claims

The question of whether an action can be characterized as a "removal" action or a "remedial" action is one of law appropriate for resolution on summary judgment. State of California v. Hyampom Lumber Co., 903 F. Supp. 1389, 1391 (E.D.Cal. 1995).

Under § 113(g)(2)(A), an action for recovery of the costs of a "removal action" must be filed within three years after "completion" of the "removal action.

"Removal" is defined by 42 U.S.C. § 9601 (23) as

  the cleanup or removal of released hazardous
  substances from the environment,
  such actions as may be necessary
  [sic] taken in the event of the threat of
  release of hazardous substances into the
  environment, such actions as may be
  necessary to monitor, assess, and evaluate
  the release or threat of release of
  hazardous substances, the disposal of removed
  material, or the taking of such
  other actions as may be necessary to
  prevent, minimize, or mitigate damage
  to the public health or welfare or to the
  environment, which may otherwise result
  from a release or threat of release.
  The term includes, in addition, without
  being limited to, security fencing or other
  measures to limit access, provision of
  alternative water supplies, temporary
  evacuation and housing of threatened
  individuals not otherwise provided for,
  action taken under section 9604(b) of
  this title, and any emergency assistance
  which maybe provided under the Disaster
  Relief and Emergency Assistance
  Act [42 U.S.C.A § 5121 et seq.].

"Removal refers to short-term action taken to halt the immediate risks posed by hazardous wastes." Fairchild Semiconductor Corp. v. United States EPA, 769 F. Supp. 1553, 1555 (N.D.Cal. 1991). "During the removal action phase, a site posing a risk of hazardous waste release is studied and various cleanup options considered." Id. The site-specific study which ensues is the RI/FS. Id. "Once the RI/FS has been completed, EPA will choose the remedial action appropriate for the site." Id. "Removal action is taken before remedial action." Id.

Defendants contend that, here, "removal" was completed more than three years before the complaint was filed. Defendants characterize the initiation of the site inspection in 1982, the removal of the two waste solvent tanks and two subsurface acid neutralization systems in 1984, and the removal of contaminated soil in 1984 as "removal action," which "culminated with a completion of a RI/FS in May, 1991," more than three years before the complaint was filed.

AMD appears to concur. See Opp. at 13:8-9 ("The activity conducted at the site between 1982 and 1991 was `removal action,' not remedial action."). However, AMD argues that, even if § 113(g)(2) does apply, a contribution claim for the "removal" activities is not time-barred under § 113(g)(2) because "remedial action" was begun within three years of completion of the "removal action." See Part II.A.5, infra.

                  4. The § 113(g)(2)(B) Limitations
                        Period for "Remedial Action"
                                Cost Claims

Under § 113(g)(2)(B), an action to recover costs of a "remedial action" must be filed "within six years after initiation of on-site construction of the remedial action. . . ." The term "remedial action" is defined by 42 U.S.C. § 9601 (24) as:

  those actions consistent with permanent
  remedy taken instead of or in addition to
  removal actions in the event of a release
  or threatened release of a hazardous
  substance into the environment, to prevent
  or minimize the release of hazardous
  substances so that they do not migrate
  to cause substantial danger to
  present or future public health or welfare
  or the environment. The term includes,
  but is not limited to, such actions
  at the location of the release as storage,
  confinement, perimeter protection using
  dikes, trenches, or ditches, clay cover,
  neutralization, cleanup of released hazardous
  substances and associated contaminated
  materials, recycling or reuse,
  diversion, destruction, segregation of
  reactive wastes, dredging or excavations,
  repair or replacement of leaking containers,
  collection of leachate and runoff,
  onsite treatment or incineration, provision
  of alternative water supplies, and
  any monitoring reasonably required to
  assure that such actions protect the public

  health and welfare and the environment. . . .

"Remedial action refers to permanent remedies taken instead of or in addition to removal, including the destruction of hazardous wastes." Fairchild, 769 F. Supp. at 1555.

Defendants contend that the "physical on-site construction" of "remedial action" activities commenced no later than 1986, when ground water extraction wells were installed in the A aquifer and the ground water treatment facility began operation. Defendants note that through June, 1997, the extraction system reportedly treated 1,775,400 gallons of ground water, and the treatment facility was reported "to be effective in removing volatile chemicals from ground water" as of August, 1987. Geselbracht Decl.Ex. B ! 2.3. Defendants conclude that the ground water extraction and treatment system constituted "cleanup of released hazardous substances" and "onsite treatment" and thus was "remedial action" as defined by 42 U.S.C. § 9601 (24).

AMD counters that these actions were "removal," not "remedial," because all actions which occur before the selection of the permanent remedy are necessarily "removal" actions, and because the RI/FS process, which was ongoing in 1986, "is a type of removal activity." Opp. at 15:5-10 (citing Kelley v. E.L. DuPont de Nemours and Co., 17 F.3d 836, 840-41 (6th Cir. 1994)). AMD contends that no "remedial" action can take place until the ROD is issued because no "remedy" has been determined until that time. "Remedial actions are generally response actions conducted in accordance with a ROD." United States v. Akzo Nobel Coatings, Inc., 990 F. Supp. 897, 904 (E.D.Mich. 1998). AMD notes that "just because what would otherwise be a removal action effects a permanent remedy does not convert that response into a remedial action." Opp. at 15 (citing U.S. Steel Supply, Inc. v. Alco Standard Corp., No. 89-C-20241, 1992 WL 229252 at *10 (N.D.Ill. Sept. 9, 1992)).

In Hyampom, cited by both parties, the suit was timely under the § 113(g)(2)(B) statute of limitations as long as the "remedial action" was initiated on or after September 30, 1988. The plaintiff argued that any activity which occurred prior to issuance of the October 19, 1988 Final Remediation Plan ("RAP") was a "removal" action as a matter of law. The court disagreed on the ground that the draft RAP, issued on June 24, 1988, had disclosed the central elements of the design of the permanent remedy. Hyampom) 903 F. Supp. at 1393. The court firmly rejected the proposition that remedial action can never occur prior to the final approval of the permanent remedy. "This would make the lengthy definition of "remedy' and "remedial action' appearing in § 9601 (24) meaningless — the terms would simply be defined as all response activities which occur after final approval of the permanent plan." Id. at 1392-93. However, the court held that fence installation which occurred "more than nine months before the Draft RAP was issued, and while RI/FS testing was still ongoing" was removal activity. "It is beyond dispute that RI/FS activities, such as the testing and monitoring that went on at the Jensen site, are `removal' activities for purposes of CERCLA, since `removal' is expressly defined to include "such actions as may be necessary to monitor, assess, and evaluate the release or threat of release of hazardous substances . . .'" Id. at 1393 (citing 42 U.S.C. § 9601 (23)). Even certain fence installation which took place after the Draft RAP was issued was deemed "removal action," because it served the purpose of securing the site while RI/FS monitoring and testing were conducted. Id. The court also noted that "fencing is specifically listed as a "removal action' in § 9601 (23)." Id.

In characterizing installation of an electrical pole and water lines on the site, on the other hand, the Hyampom court noted that, had those utilities been connected while on-site assessments and evaluations were still ongoing, "the installation would in all likelihood be characterized as a `removal' action." Id. The court also noted that although § 9601 (23) (defining "removal" action) does not specifically list utility installation, utilities could fall within that section's catch-all phrase, "such actions as may be necessary [sic] taken in the event of the threat of release of hazardous substances into the environment." Id. However, the court found that "the utilities played a critical role in the implementation of the permanent remedy," and there was no evidence that they were used for any "removal" purpose whatsoever. Id. The Water and power lines were installed for the "sole purpose of providing power and water to the Jensen site during the implementation of the permanent remedy," and "water and power were central to various aspects of the remedy, including fire control, dust suppression, steam cleaning, and lighting." Id. at 1394. The utility installation was therefore "remedial," not "removal" activity, and "remedial action" therefore began' on September 15, 1988, the date that utility installation work was initiated. Id.

Under Hyampom, therefore, several factors assist in the characterization of an action as "removal" or "remedial": (1) proximity to disclosure of the final remedial design, which may occur prior to approval of the final remedial plan, (2) whether RI/FS monitoring and testing are ongoing at the time of the action, (3) whether the action falls within the statutory definition of "removal" (or "remedial") and (4) the action's role in the implementation of the permanent remedy.

The Seventh Circuit's decision in United States v. Navistar Int'l Transportation Corp., 152 F.3d 702 (7th Cir. 1998) comports with that of the Eastern District of California in Hyampom. In Navistar, as in Hyampom) the plaintiffs argued that the court should establish a rule that "remedial action" cannot begin until the EPA issues final, written approval of the remedial design. The court declined to adopt such a "bright-line" rule. Navistar, 152 F.3d at 711 ("If [Congress] had intended to require that the EPA issue its final approval of the remedial design in order for a "remedial action' to begin . . . Congress surely would have provided us with a more explicit direction to that effect."). The court explained that a "remedial action" is one that is "consistent with" the particular permanent remedy that has been developed for the site. Id. at 712. Because "[i]t is undisputed that the remedial action for the site called for the construction of a permanent clay cap," that construction was "remedial action," and the statute of limitations began to run on the date construction of the cap was initiated. Id. at 713. Although the Navistar court did not discuss when the design of the remedy was first disclosed, final written approval of the remedy was issued just two days after the clay cap construction was initiated. Id. at 705, 713.

Here, defendants argue that "remedial" action was initiated at the Site no later than April, 1986, when wells were drilled for the water extraction system. Looking to the first factor addressed by the Hyampom court, proximity to disclosure of the final remedial design, no evidence of a "draft" of the plan of remediation has been submitted to the court. The April, 1991 RI/FS reveals that, four years after the 1986 water extraction activity was initiated, different alternatives for final remedial action were still being proposed and evaluated. The evidence indicates that design of the final remedy was not disclosed until the September, 1991 ROD issued.

With regard to the second factor addressed by Hyampom, whether RI/FS monitoring and testing were ongoing at the time of the activity, investigation at the Site began in 1982, and Site testing was still being conducted in November of 1989. Allison Decl.Ex. A at 16; Content Decl.Ex. 1 at 19 ("Soil sampling programs at AM-Arques began in 1982 and have been conducted as recently as November 1989, under RWQCB oversight, to identify source areas for soil and groundwater contamination."). Evaluation and analysis of the testing results were not completed until the RI/FS issued in April, 1991. The technical information gathered by AMD and provided in the RI/FS was reported to be "`acceptable for developing a final cleanup plan" only as of the September 20, 1991 RWQCB Order No. 91-139.

With regard to the third Hyampom factor, whether the action falls within the statutory definition of "removal" or "remedial," installation of the water extraction system could constitute "cleanup of released hazardous substances" under the § 9601 (24) definition of "remedial action." The evidence includes numerous references to the extraction system installation prior to the ROD as a "remedial measure" or an "interim remedial measure." See, e.g., Content Decl.Ex. 2 at 1; Allison Decl. Ex. A at ES-4. Further, the ROD states that the purpose of the extraction and treatment system initiated in 1986 was "to control contaminant migration in the subsurface [and] control contaminant transport," (Content Decl.Ex. 1 at 18) a purpose which comports with the § 9601 (24) definition of "remedial action," as one taken "to prevent or minimize the release of hazardous substances so that they do not migrate to cause substantial danger. . . ." However, the court also notes that in Hyampom, the utility installation was "remedial" even though it could fit within the statutory definition of "removal." Hyampom, 903 F. Supp. at 1393.

The fourth consideration discussed in Hyampom is the action's role in the implementation of the permanent remedy. Although the well extraction system at the Site was ultimately expanded as part of the permanent remedy, the system could not, upon its installation, have "played a critical role in the implementation of the permanent remedy," because the permanent remedy was not determined until four years later. The ROD reports that the extraction system was implemented "with the goal of controlling further contamination migration while ongoing site investigations continued to collect the data necessary for final remedy selection." Content Decl.Ex. 1 at 20. In Hyampom, it had been clear at the time that the utilities were installed that they were "central parts of the "construction of the permanent remedy'" because the Draft RAP had by that time disclosed what the design of the final remedy was. Here, the design of the final remedy had not been developed or disclosed when the extraction wells were installed at the Site in 1986, and there is no evidence that they were disclosed before September, 1991. The fact that the extraction activities ultimately did not turn out to be "short-term," because they were implemented in the final remedy four years later, cannot now be considered in hindsight.

Under Hyampom and Navistar, the formal adoption of the final remedy is not a "bright-line" cut-off between "removal" and "remedial action." Id. at 1392-93; Navistar, 152 F.3d at 711. However, here, the September 21, 1991 ROD was the first statement of what the final remedy was to be. No final remedy design, in draft form or otherwise, was apparently issued until September 21, 1991. "Remedial action" could not take place until that design was known, and until the RI/FS assessment process had reported sufficient information to allow for design of the remedy.

5. Recovery of "Removal Action" Costs

Section 113(g)(2)(B) provides that "if the remedial action is initiated within 3 years after the completion of the removal action, costs incurred in the removal action may be recovered in the cost recovery action brought under this subparagraph." AMD contends that "the removal action was completed with the RI/FS and ROD process in September, 1991." Opp. at 22:8-10. Defendants agree that the removal action "was `completed' in 1991 when the RI/FS was completed," but claim that the remedial action was not initiated three years after that removal action because the remedial action, which commenced in 1986 according to defendants, preceded the removal action. Memorandum of Points and Authorities in Support of Defendants' Motion for Partial Summary Judgment at 8-9. The court has herein concluded that removal activity was completed, and remedial action commenced, in September, 1991. See Part II.A.4, supra. The removal and remedial actions were therefore within three years of each other, and the action for contribution for removal costs is timely under § 113(g)(2)(B).

                    B. AMD's Fourth and Fifth Causes of
                       Action for Contribution Under
                                 State Law

Defendants claim that the California Code of Civil Procedure §
388(a) three-year statute of limitations for actions "based upon a liability
created by statute" applies to AMD's fourth and fifth causes of action
for contribution under California health & Safety Code § 25363. AMD
claims that 06 applicable statute of limitations is "one year or two"
under Mangini v. Aerojet-General Corp., 230 Cal.App.3d 1125,  1154-55,
281 Cal.Rptr. 827 (1991), aff'd, 12 Cal.4th 1087, 51 Cal.Rptr.2d 272,
912 P.2d 1220 (1996), and that the period runs from the time each payment
was made by the claimant.*fn7 "In the absence of a contrary statutory
command, a cause of action for equitable indemnity does not come into
existence until the indemnitee has suffered loss through payment." Id. at
1154, 281 Cal.Rptr. 827. Here, however, AMD's claim is not a common law
claim for equitable indemnity as was the case in Mangini, it is brought
under statute. In Acme Fill Corp. v. Althin CD Medica4 Inc., 1995 WL
822665 (N.D.Cal.), this court held that a claim under Cal. Health &
Safety § 25363 accrues at the same time as a CERCLA contribution
claim, since the California Hazardous Substance Account Act (Cal. Health
& Safety Code § 25300 et seq.) is patterned directly on CERCLA. There
is, therefore, a "contrary statutory command" here, and the fourth and
fifth causes of action accrued, like the CERCLA causes of action, in
September of 1991. The Cal.Code Civ.Proc. § 388(a) three-year
statute of limitations applies to claims under Cal. Health & Safety Code
§ 25363. Acme, 1995 WL 822665 at *4. Therefore, the complaint, filed
in September of 1997, is untimely as to the fourth and fifth causes of
action.

                     C. AMD's Seventh and Eighth Causes
                  of Action for Negligence and Negligence
                                   Per Se

Defendants argue that AMD's seventh and eighth causes of action are barred by the Cal.Code Civ.Proc. § 338(b) three-year statute of limitations, since AMD suspected alleged damage and began investigation no later than 1983.*fn8 A cause of action for negligence arising from alleged property damage due to hazardous waste contamination accrues when the plaintiff discovers the injury and its cause, or should have through the exercise of reasonable diligence. Mangini, 230 Cal. App.3d at 1150, 281 Cal.Rptr. 827. In Mangini, the court held that the cause of action accrued when "plaintiffs had sufficient information to put them on notice of the possibility that defendant had dumped hazardous waste on their land." Id. at 1152-53, 281 Cal.Rptr. 827. Here, regardless of whether the investigation begun in the early 1980's would trigger the statute of limitations, there can be no dispute that as of at least September 1991, after the RI/FS investigation and testing process was complete and the ROD was issued, AMD was on notice of defendants' potential responsibility for hazardous waste at the Site. The negligence claims, filed six years later, are barred by Cal.Code Civ. Proc. § 338(b). Summary judgment is therefore granted as to the seventh and eighth causes of action.

                     D. AMD's Eleventh Cause of Action
                            for Attorneys' Fees

AMD's eleventh cause of action is for an award of attorneys' fees under
California Code of Civil Procedure § 1021.5. That section provides
that a court may award attorneys' fees to a successful party in a
"private attorney general" action which (a) enforces an important right
affecting the public interest, and (b) confers a significant benefit
(pecuniary or nonpecuniary) upon the general public or a large class of
persons, if (c) the necessity and cost to plaintiff in bringing its
private enforcement action outweighs its stake in the action. Cal.Code
Civ.Proc. § 1021.5; Woodland Hills Residents Ass'n v. City Council,
23 Cal.3d 917, 934-35, 154 Cal.Rptr. 503, 593 P.2d 200 (1979); Beach
Colony II v. Coastal Comm'n, 166 Cal.App.3d 106,  110, 212 Cal.Rptr. 485
(1985).

  The purpose of an award of attorney
  fees pursuant to section 1021.5, is to
  encourage suits that enforce "common
  interests of significant societal importance,
  but which do not involve any individual's
  financial interest to the extent
  necessary to encourage private litigation
  to enforce the right. To encourage such
  suits, attorney fees are awarded when a
  significant public benefit is conferred
  through litigation pursued by one whose
  personal stake is insufficient to otherwise
  encourage the action. Section
  1021.5 was not designed as a method for
  rewarding litigants motivated by their
  own pecuniary interests who only coincidentally
  protect the public interest."

Satrap v. Pacific Gas and Electric Co., 42 Cal.App.4th 72, 78,
49 Cal.Rptr.2d 348 (1996) (citing Beach Colony II, 166 Cal. App.3d at
114, 212 Cal.Rptr. 485) (internal citations omitted). Therefore, where
the primary effect of a lawsuit is to advance or vindicate a plaintiffs
personal economic interests, an award of fees under § 1021.5 is
improper, even if some incidental public benefit derives from the suit.
Flannery v. California Highway Patrol, 61 Cal.App.4th 629,  635,
71 Cal.Rptr.2d 632 (1998); Kaufman and Broad-South Bay v. Unisys Corp.,
822 F. Supp. 1468, 1478, (N.D.Cal. 1993), disapp'd on other grounds, KFC
Western) Inc. v. Meghrig, 49 F.3d 518 (9th Cir. 1995). A § 1021.5
request for attorneys' fees may be denied where the potential recovery of
damages creates sufficient financial incentive to bring the lawsuit. See
Satrap v. Pacific Gas and Electric Co., 42 Cal.App.4th 72, 78,
49 Cal.Rptr.2d 348 (1996) (discussing Luck v. Southern Pacific
Transportation Co., 218 Cal.App.3d 1, 267 Cal.Rptr. 618 (1990)).

Here, AMD seeks recovery of its cleanup costs from defendants. Although the cleanup itself may have conferred an incidental benefit on the public, AMD had a strong personal, financial incentive to bring suit, namely, to recover the amounts it has expended cleaning the Site. Further, as defendants argued at the hearing on this motion, the public derives no particular benefit if AMD ultimately prevails in this action, for the Site cleanup has or will occur regardless of whether it is AMD or defendants that are ultimately responsible for paying for it. AMD's suit, as distinguished from the cleanup activities which underlie it, confers no significant benefit upon the general public. Defendants' motion is therefore granted as to the eleventh cause of action.

E. ORDER

For the foregoing reasons, the court grants defendants' motion in part and denies it in part. Summary judgment is granted as to the fourth, fifth, seventh, eighth and eleventh causes of action. Summary judgment is denied as to the first and third causes of action.


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