ORDER DENYING MOTION TO DISMISS
Re: Dkt. No. 13
Plaintiffs San Francisco Herring Association (“SFHA”) and Dan Clarke brought a complaint against defendants Pacific Gas and Electric Company and PG & E Corporation (collectively, “PG & E”) arising from PG & E’s operation of manufactured gas plants roughly one hundred years ago. Although these plants no longer exist, they allegedly left behind substantial quantities of waste products that continue to contaminate the land in the Marina and Fisherman’s Wharf neighborhoods of San Francisco and the water of the San Francisco Bay. According to the complaint, the defendants failed to conduct adequate testing or remediation to eliminate the danger this waste poses to the environment.
The defendants move to dismiss the plaintiffs’ causes of action for violations of the Clean Water Act (“CWA”) and the Resource Conservation and Recovery Act (“RCRA”), alleging that the plaintiffs lack standing and that they fail to state a claim upon which relief can be granted. The plaintiffs plausibly allege injury in fact and the factual basis for the challenged causes of action. Therefore I DENY PG & E’s motion to dismiss.
BACKGROUND
For purposes of PG & E’s motion, I take the allegations of the complaint, which I summarize in the next five pages, as true. The defendants owned and operated manufactured gas plants (“MGPs”), highly polluting, low-tech refineries used in the nineteenth and early twentieth centuries to create gas from coal (or a combination of coal and oil, or other solid fuel sources). Compl. ¶¶ 2, 20 (Dkt. No. 1). MGPs often spread across several city blocks, and consisted of multiple operations and buildings known as “gas works.” Id. ¶ 22. Coal was “gasified” by heating it in oxygen-poor ovens. The fuel gases generated were then purified of unwanted compounds be
The reduction process created considerable solid and gaseous toxic waste. Id. ¶ 24. The waste produced was allowed to leach into the ground, dumped into waterways, or buried onsite. Id. ¶27. These wastes allegedly still contaminate the sites of former MGPs and the areas where the waste was deposited. Id.
Among the most problematic types of waste are coal residue solids and coal tar, because they contain chemicals known as polycyclic aromatic hydrocarbons (“PAHs”). Id. PAHs are both lipophilic (easily dissolvable into fats, allowing them to cross biological membranes and accumulate inside organisms) and genotoxic (able to damage genetic information once accumulated inside an organism’s cells, causing mutations). Id. Many PAHs associated with MGP waste are known carcinogens, and identified by the United States Environmental Protection Agency (“EPA”) as toxic pollutants under 40 C.F.R. § 401.15. Id. Groundwater and above-ground water, contaminated soils, and toxic vapor commonly transport PAHs. Id. ¶ 29.
MGPs were often situated in close vicinity to residential areas. Id. ¶ 21. The plaintiffs specifically point to the modern-day footprints of three MGPs: the North Beach MGP, the Fillmore MGP, and the Beach Street MGP. Id. ¶ 1. The North Beach MGP was comprised of at least four city blocks, bounded by Marina Boulevard, Buchanan Street, North Point Street, La-guna Street, Bay Street, and Webster Street. Id. ¶ 31. Immediately west of the MGP was a canal opening, up to the San Francisco Bay that was filled in 1912. Id. ¶ 34. PG & E owned and operated this site until at least April 1906. Id. ¶ 31.
The Fillmore MGP was comprised of at least four city blocks, bounded by Fillmore Street, Cervantes Street, Mallorca Way, Pierce Street, and Toledo Way. Id. ¶ 36. PG & E owned and operated this site until at least April 1906. Id.
The Beach Street MGP was comprised of an area near Beach Street and Powell Street in the Fisherman’s Wharf neighborhood. Id. ¶ 43. PG & E owned and operated the site until at least the mid-1950s, when the property was sold and redeveloped for commercial use. Id. The Radis-son Hotel Fisherman’s Wharf currently occupies portions of the site. Id. ¶ 86.
All of the subject MGP facilities were either abutting the San Francisco Bay shoreline or within a few hundred feet of it at the time of operations. Id. ¶ 86.
I. MGP WASTE CONTAMINATION
A. Contamination at Clarke’s home
, Plaintiff Clarke’s home is a 0.08-acre parcel within the footprint of the North Beach MGP. Id. ¶ 55. There is historical evidence that a coal bin was located in the vicinity of the home during the time that the MGP was in operation. Id. ¶ 56. Small, lightweight “black rocks” are found in the home’s backyard in shallow soil. Id. They are typically similar in appearance to raw unprocessed coal or to solids reformed from a liquid state. Id. In March of 2010, Clarke discovered two unusually large black rocks and handed them over to PG & E for testing. Id. ¶ 57. Test results indicated that the rocks contained MGP waste, and that their toxicity was “very high.” Id. Samples taken from one rock tested positive for several PAH compounds. Id. ¶ 58. More black rocks were discovered in 2013, when an emergency sewer repair opened a small hole in the slab underneath
PG & E tested samples of Clarke’s soil, which revealed “significant” MGP waste, and showed that the contamination is widespread across the entire footprint of the home. Id. ¶ 60. All locations from which soil samples were taken had high levels of benzo(a)pyrene equivalent (“B(a)P-EQ”), which indicates the degree of toxicity. Id. ¶ 62. The California EPA uses a target of 0.9 ppm for B(a)P-EQ as the allowable limit. Id. ¶ 61. A standard of 0.038 ppm of B(a)P-EQ is equal to a one in 1 million incremental risk- of cancer. Id. ¶ 64. At Clarke’s home, the B(a)P-EQ levels tested as high as 1,149 ppm — or more than 1 in 100 risk of cancer. Id.
B. Contamination of San Francisco Bay
According to the complaint, the natural hydrologic connection between the contaminants in groundwater and soil and the San Francisco Bay conveys MGP waste to the Bay. Id. ¶¶ 9, 54, 88-91. Another connection is man-made: in the 1970s, the City and County of San Francisco (“CCSF”) constructed a combined sewer and storm-water collection system to transport waste to water treatment plants. Id. ¶ 93. A network of combined transportation and storage (“T/S”)' boxes was constructed along the perimeter of the San Francisco Bay. Id. The plaintiffs allege that the T/S network conveys MGP waste to the Bay in three ways: (i) via groundwater that flows at or near the subject MGP sites and eventually enters the T/S network; (ii) via groundwater washed into the T/S system during large storm events; and (iii) via the T/S network itself, as the water treatment process does not remove PAHs from water before it is discharged into the Bay. Id. ¶¶ 93-98.
Pacific herring are adversely affected by MGP waste discharged inte the Bay. Id. ¶ 99. Herring traditionally have very high levels of productivity, and are an important commercial species and source of food for other species. Id. ¶¶ 108-09. However, PAHs are known to have “devastating” effects on herring, as they kill fertilized eggs and larva on contact or through photo-enhanced toxicity.
Herring born in the Bay return to spawn there for up to eight years, traditionally along waterfront areas adjacent to the subject MGP sites. Id. ¶¶ 101, 109. Exposure to PAHs “both kills off a large portion of exposed fertilized eggs and larva and weakens those fish that survive the initial insult, decreasing the long-term survival of the fish, which, in turn, decreases the period of ecological services that the fish can provide.” Id. ¶ 103. Because herring is a keystone species, a loss of fertilized herring eggs or larval herring is likely to have significant negative consequences for the species and for the pelagic food web almost indefinitely into the future. Id. ¶¶ 108-10.
II. TESTING FOR MGP WASTE CONTAMINATION
The plaintiffs assert that PG & E has conducted only “piecemeal testing” for MGP wastes in various areas near • the subject MGP sites. Id. ¶ 88. Where such testing has been done, by either PG & E or CCSF, high levels of PAHs have been discovered. Id. In groundwater in and around the subject MGP sites, including Clarke’s home, high levels of PAH contamination as a result of MGP waste have been shown. Id. ¶ 92. PAHs have also
A. Testing near North Beach MGP
Testing by CCSF over the past two •decades near Gashouse Cove, a harbor in the San Francisco Bay, revealed that sediment in the tidal and submerged lands in an inlet bordering the North Beach MGP site is heavily contaminated with PAH-laden waste. Id. ¶¶ 69-72. There is also evidence of a significant deposit of coal tar seeping into the Bay. Id. ¶¶ 73-74. The testing determined that the waste migrated into the inlet from upland sources. Id. ¶ 70.
Testing near the Marina substation, which is a PG & E-owned 0.25 acre parcel within the North Beach MGP footprint, revealed PAHs in unsaturated soil, saturated soil, and groundwater found on site. Id. ¶ 75. Further testing in another 0.3-acre parcel within the MGP footprint that previously functioned as the headquarters of the gasworks revealed the presence of “significant” amounts of PAHs in shallow soil and groundwater. Id. ¶ 76. The contamination was attributed to waste product from coal gasification, similar to the black rocks found at Clarke’s home. Id.
Every residence in the footprint of the North Beach MGP, including Clarke’s home, that has been tested for contamination has required major remediation. Id. ¶ 77. Thus far, there have been six remediations, all of which have been accompanied by a requirement that the property owner enter into a land usd covenant (“LUC”) with PG & E that restricts future use of the property. Id.
B. Testing near Fillmore MGP
Testing by CCSF in 1977 in preparation for construction of a combined sewer and storm water storage and transport system in the. Marina neighborhood revealed “creosote residue” at multiple depths along Marina Boulevard. Id. ¶ 80. Creosote is a chemical substance that is created by the high-temperature treatment of sources such as coal, beech, or resin. Public Health Statement for Creosote, U.S. AgenCy FOR Toxic Substanoes & Disease Registry (Sept.2002), http://www.atsdr.cdc.gov/phs/ phs.asp?id=64& tid=18. The report for the study stated that the contamination “probably resulted] from previous gas plant activities.” Compl. ¶ 80. The U.S. Geological Survey also noted a “creosote smell” in the same area. Id. ¶¶ 82-83. When CCSF conducted testing of the sediment in the West Basin Marina in 2011, it found PAH contamination in two areas designated as “not suitable for unconfined aqua disposal.” Id. ¶ 84.
Ten residences within the Fillmore MGP footprint have known test results at this time. Id. ¶ 85. Out of the ten, seven required major remediation with an LUC, and one required an LUC but not remediation. Id. Two properties do not require an LUC or remediation, but it is not clear that they are uncontaminated with MGP waste. Id.
C.Testing near Beach Street MGP
At the Radisson hotel, currently located on the former Beach Street MGP, groundwater and soil testing in 1997 revealed “exceptionally high PAHs in soil and severe contamination of several kinds in groundwater, attributable to the Beach Street MGP.” Id. ¶86. B(a)P-EQ was found in concentrations of up to 45,000 mg/kg. Id. Testing in 2012 at Pier 39 found elevated levels of PAH in marina sediment samples. Id. ¶ 87. The B(a)PEQ concentrations were measured at 45,-000 ppm, or a 1 in 10 incremental risk of cancer. Id. The same areas were dredged and retested in 2013 and elevated levels of
III. PROCEDURAL BACKGROUND
The plaintiffs submitted a Notice of Intent to Sue letter (“NOI”) to PG & E on April 29, 2014. NOI (Dkt. No. 13-2).
LEGAL STANDARD
Under Federal Rule, of .Civil Procedure 12(b)(6), .a district court must dismiss a complaint if it fails to state a claim upon which relief can be granted. To survive a Rule 12(b)(6) motion to dismiss, the plaintiff must allege “enough facts to state a claim to relief that is plausible on its face.” Bell Atl. Corp. v. Twombly,
In-' deciding whether the plaintiff has stated a claim upon which relief can be granted, the court accepts the plaintiffs allegations as true and draws all reasonable inferences in its favor. See Usher v. City of Los Angeles,
“For purposes of ruling on a motion to dismiss for want of standing, both the trial and reviewing courts must accept as true all material allegations of the complaint and must construe the complaint in favor of the complaining party.” Maya v. Centex Corp.,
DISCUSSION
I. NOTICE
PG & E argues that there was insufficient notice in the plaintiffs’ NOI to establish subject matter jurisdiction because the plaintiffs failed to adequately identify a
Notice regarding an alleged violation of the CWA or RCRA requires “sufficient information to permit the recipient to identify”:
[T]he specific [effluent] standard, limitation, or order alleged to have been violated, the activity alleged to constitute a violation, the person or persons responsible for the alleged violation, the location of the alleged violation, the date or dates of such violation, and the full name, address, and telephone number of the person giving notice.
40 C.F.R. § 135.3(a); see also 40 C.F.R. § 254.3(a).
Under the CWA, a plaintiff must provide notice of the alleged violation to the EPA, to the state in which the alleged violation occurred, and to the alleged violator. 33 U.S.C. § 1365(b)(1)(A). Where a citizen enforcement action fails to comply with CWA notice requirements, the district court lacks subject matter jurisdiction and must dismiss the action. See Fed. Rule Civ. P. 12(b)(1); Natural Res. Def. Council v. Sw. Marine, Inc.,
CWA notice requirements are mandatory and must be strictly construed. Hallstrom v. Tillamook Cnty.,
PG & E does not contend that the plaintiffs failed to specify the nature of or the dates of the alleged CWA violations. Instead, it asserts that the NOI did not identify the T/S system as a potential point source or as a manner and method by which MGP waste in groundwater is transported to the Bay. Mot. 9,
While the NOI was indeed silent as to the T/S system, that silence is not material to the CWA notice requirements. The T/S system is alleged as one pathway by which PAHs are discharged into the Bay. This fact does not change the complaint’s basic argument about the specific effluent standard that was violated, the activity constituting a violation, the persons responsible for the violation, or the location and dates of the violation. See 40 C.F.R. §§ 135.3(a), 254.3(a). Moreover, the plaintiffs identify the MGPs, and not the T/S system, as the relevant point sources in the complaint and the NOI. Compl. ¶ 217; NOI at 2-3.
The NOI provided PG & E with adequate information to identify the violation — namely, the discharge of MGP waste into the San Francisco Bay and the ongoing presence of PAHs in groundwater and
II. STANDING
In order to have standing under Article III, a plaintiff must show: (i) that he has suffered an “injury in fact” that is (a) concrete and particularized and (b) actual or imminent, not conjectural or hypothetical; (ii) the injury is “fairly traceable” to the challenged action of the defendants; and (iii) that a favorable decision will be likely to redress the injury. Friends of the Earth, Inc. v. Laidlaw Env’t Services (TOC), Inc.,
With respect to the CWA claims, PG & E argues that SFHA failed to establish the second and third requirements of standing. Mot. 17. PG & E’s arguments are meritless. The complaint states that SFHA’s members’ livelihoods depend on the continued productivity and abundance of herring in the San Francisco Bay. Compl. ¶ 9. The increase in PAH levels in the Bay threatens the herring population, and is in-turn caused by the discharge, without a permit,, of PAHs from former MGP sites that PG & E owned and operated. Id. ¶¶ 9, 107, 212-19. The connection between the MGP waste and the heightened level of PAHs in the Bay is corroborated by allegations that testing done by PG & E and CCSF have demonstrated high levels of toxicity and contamination. Id. ¶¶ 92-98. SFHA has adequately pleaded that PG & E discharged a pollutant into the Bay that causes or contributes to its injuries. See Sw. Marine,
SFHA has also satisfactorily requested redress under the CWA. It describes a continuing violation and seeks an injunction to compel PG & E to remediate the MGP waste purportedly endangering the environment of the Bay. Compl. ¶¶ 70, 87-88; see also Sw. Marine,
With respect to Clarke’s claim under the CWA, PG & E argues that the complaint does not establish the “injury-in-fact” element of standing. Mot. 17-18. It asserts that Clarke’s injury does not relate to navigable waters as required by the CWA and cases such as Ecological Rights Foundation v. Pacific Lumber Co. Id.;
Ecological Rights Foundation and most other cases discussing the “injury-in-fact” requirement address the standing of individuals who had a recreational interest in the allegedly contaminated navigable water. See, e.g.,
The complaint states that Clarke’s property is located within the historic footprint of the North Beach MGP point source. Compl. ¶¶ 55, 231. The waste on his property came in several forms and was “created, handled, stored, transported and/or disposed of at various locations within the grounds of the Subject MPG [sic] Site and/or in the vicinity thereof.” Id. ¶¶ 27, 49. It was also allegedly transported onto Clarke’s property from the groundwater. Id. ¶¶211, 230. Clarke has thus established an injury related to the point source and the conduit of the alleged CWA violations, but not to the relevant body of navigable water — the San Francisco Bay.
Although few courts have addressed this specific issue, cases indicate that a plaintiff bringing a CWA citizen suit can establish standing based upon a broad category of injuries. See e.g., Sierra Club v. U.S. Army Corps of Eng’rs,
Moreover, courts construe CWA standing liberally in other circumstances. For instance, a citizen may establish standing based upon “recreational use” of an affected body of water by demonstrating only that he or she “suffer[s] in his or her degree of aesthetic or recreational satisfaction.” Envtl. Prot. Info. Ctr.,
In this case, the defendants’ alleged action that violates the CWA is the “disc-harg[e][of] pollutants into the waters of the United States without a permit.”
PG & E also attacks SFHA’s standing to bring its RCRA claim, arguing that “land-based harms” are not germane to SFHA’s organizational purpose. Reply 4. This position is groundless. The gravamen of SFHA’s complaint involves MGP waste that originated on land and is transmitted into the Bay. The fact that some of the contamination initially occurred on land is not inconsistent with SFHA’s goal of protecting the San Francisco herring fishery. See Compl. ¶ 7. Therefore, SFHA has standing to bring its claim under the RCRA.
III. CWA CLAIMS
The CWA “aims to restore and maintain the chemical, physical and biological integrity of [the] Nation’s waters.” Ass’n to Protect Hammersley v. Taylor Res.,
PG & E argues that both plaintiffs have failed to state a claim for relief under the CWA for three reasons: (i) the claims describe wholly past violations, (ii) the plaintiffs inappropriately identify MGPs as “point sources” of the pollution, and (iii) the claims largely relate to groundwater, which is not considered “navigable water” subject to CWA protection. Mot. 12-17.
A. Plaintiffs adequately alleged ongoing violations
PG & E contends that the violations alleged in the complaint are “wholly past.” Mot. 12. It points to the fact that the MGP operations terminated between 84 and 106 years ago, and argues that the “migration of residual contamination from previous releases does not constitute an ongoing discharge.” Id. at 13. Plaintiffs disagree, arguing that groundwater continues to transport the contaminants to the Bay, thereby creating an ongoing violation. Oppo. 18.
“[C]itizens ... may seek civil penalties only in a suit brought to enjoin or otherwise abate an ongoing violation.” Gwaltney,
Both parties spend much time debating whether the waste from the long-defunct MGP operations constitutes an ongoing discharge. However, I consider this dispute to be factual in nature, and improper to consider on a motion to dismiss. See Sierra Club,
Significantly, the complaint also alleges that PG & E’s current behavior contributes to ongoing violations relating to the MGP discharges.' It provides that PG & E’s refusal to test for contaminants in groundwater that serves as a conduit means that MGP sites will “continue to present an imminent and substantial endangerment to human health and the environment. ...” Id. ¶ 169 (emphasis added); see also Marrero Hernandez v. Esso Standard Oil Co. (Puerto Rico),
B. Plaintiffs sufficiently identified a point source of the contamination
Only discharges of pollutants from “point sources” fall within the purview of the NPDES program. 33 U.S.C. § 1311(a). The CWA defines a “point source” as:
[A]ny discernible, confined and discrete conveyance, including but not limited to any pipe, ditch, channel, tunnel, conduit, well, discrete fissure, container, rolling stock, concentrated animal feeding operation, or vessel or other floating craft, from which pollutants are or may be discharged. This term does not include agricultural stormwater discharges and return flows from irrigated agriculture.
The statutory definition of a point source is meant to be “extremely broad.” Borden Ranch P’ship v. U.S. Army Corps of Eng’rs,
PG & E argues that the plaintiffs inappropriately identified the three subject MGP sites as “point sources” under the CWA. Mot. 13-16. It focuses on the definition of “point source” as a “confined and discrete conveyance,” arguing that the designation of an entire MGP site is overly broad and does not specify a “conveyance” by which pollutants are discharged. Id. at 14-15. In addition, the defendants argue that the MGPs are not sufficiently definite to allow the defendants to eliminate discharge if the court orders injunctive relief. Id. at 15.
Many of the defendants’ arguments, while appropriate in a motion for summary judgment, cannot be resolved on a motion to dismiss. I decline to hold as a matter of law that an entire factory or plant cannot be considered a “point source” under the CWA. See, e.g., Williams Pipe Line Co. v. Bayer Corp.,
Moreover, the defendants’ argument that they do not control the MGPs does not support their position. At the time of the operations, the defendants had control over the MGPs, such that they would have been able to comply with a court order that required them to cease the allegedly unlawful activities. If the-plaintiffs had alleged a more specific conveyance as a point source — the North Beach MGP tar well, for instance — there would still be an issue as to whether PG & E currently has control over the point source since it no longer owns that property. At any rate, the plaintiffs have requested that PG & E remediate the contaminated land and take steps necessary to prevent re-contamination. This remedy is potentially applicable to the entirety of the MGP sites and could be controlled by the defendants. Taking the pleaded facts as true, the plaintiffs have alleged a proper point source through which the defendants are discharging contaminants into the Bay.
C. Plaintiffs properly alleged that the San Francisco Bay is a navigable water of the United States
Finally, PG & E argues that plaintiffs’ CWA claims improperly relate to groundwater contamination, and that groundwater is not “navigablé water” covered by the CWA. Mot. 16-17. “Navigable waters” are defined in the CWA as “waters of the United States.” 33 U.S.C. § 1362(7); see also 40 C.F.R. § 122.2.
Notwithstanding the defendants’ arguments, it is clear that the plaintiffs designate the San Francisco Bay, and not groundwater, as the navigable water that is affected under the CWA. The complaint plainly alleged that the discharge of pollutants into the Bay constitutes the CWA violation. Compl. ¶219. This is further supported by the NOI, which stated that the San Francisco Bay was the navigable water. NOI at 11 (“The San Francisco Bay ... qualifies as navigable waters of the United States.”).
As the plaintiffs point out, this case is similar to Hawai’i Wildlife Fund v. Cnty. of Maui. In that case, the court rejected a similar argument because “[p]laintiffs do not appear to be arguing that the groundwater requires protection for its own independent ecological value. Instead, the concern is that the County should not be allowed to pollute the ocean through that groundwater.”
IV. RCRA CLAIMS
“The factual allegations necessary to support a claim under the RCRA are: (1) that the defendant has generated solid or hazardous waste, (2) that the defendant is contributing to or has contributed to the handling of this waste, and (3) that this waste may present an imminent and substantial danger to health or the environment.” KFD Enterprises, Inc. v. City of Eureka, No. C 08-4571 MMC,
A. The complaint adequately alleges a violation of the RCRA on behalf of Clarke
The parties do not appear to dispute (i) that PG & E generated solid or hazardous waste, and (ii) that PG & E contributed to the handling of this waste. Instead, they argue whether Clarke has established an “imminent and substantial danger.” PG & E contends that Clarke’s RCRA claims fail because it offered to remediate Clarke’s property and remove contamination to a depth of up to five feet in the yard and 12 inches beneath the house. Mot. 20. It contends that this was sufficient to remove any imminent and substantial danger. Id. at 21.
First, it is not clear that Clarke’s failure to accept PG & E’s offer of remediation renders his claims invalid. PG & E has not cited any authority for its suggestion that a plaintiff cannot plead imminent and substantial endangerment if he has rejected offers for remediation that would have removed that endangerment. See id. But obviously, if PG & E’s offered remediation would remove all imminent and substantial danger from Clarke’s home, then Clarke’s RCRA claim may fail. See, e.g., W. Coast Home Builders, Inc. v. Aventis Cropscience USA Inc., No. C 04-2225 SI,
By contrast, if PG & E’s proposed remediation would be insufficient under the RCRA to remove any immediate and substantial danger, then Clarke’s cause of action survives. See, e.g., Interfaith Cmty. Org. v. AlliedSignal, Inc.,
The complaint alleges that PG & E’s proffered remediation was inadequate. Compl. ¶¶ 18491. Clarke has asserted facts that, if true, allow a reasonable inference of immediate and substantial danger on his property. At this stage of the proceedings, there is an ongoing factual dispute as to whether PG & E’s proposed remediation would remove any imminent and substantial endangerment. Therefore, it is not appropriate to dismiss Clarke’s claims under the RCRA.
The defendants also request that this court strike Clarke’s claim under the RCRA as it relates to the Fillmore and Beach Street MGPs. Mot. 22.
The complaint alleges that Clarke suffered a concrete and particularized injury, in the form of waste contamination on his property. It does not specify that this injury results from PG & E’s activities on the North Beach MGP only; rather, it discusses “MGP Waste migrating from other locations into the Clarke Home via ground water or another mechanism.” Compl. ¶ 189 (emphasis added); see also id. ¶¶ 209-13. After discovery, it may well be the case that the Fillmore and Beach Street MGPs can be eliminated as a source of the waste contamination on Clarke’s property. But taking the allegations in the light most favorable to the plaintiffs, Clarke has stated a claim upon which relief can be granted under Rule 12(b)(6). There are insufficient grounds to strike the portion of his RCRA claim with respect to the Fillmore and Beach Street MGPs, as these allegations are not “redundant, immaterial, impertinent, or scandalous.” Fed. R. Civ. P. 12(f). The issue of whether wastes from all MGPs could migrate to Clarke’s property presents a factual question that cannot be resolved at this time. The defendants’ request to dismiss or strike is denied.
B. SFHA’s RCRA claim is precluded by the CWA
The defendants argue that SFHA’s RCRA claim fails for several reasons. First, they argue that the claim is insufficiently well-pleaded because “it is unclear from the Complaint what SFHA seeks to remedy with its RCRA claim.” Reply 4. The complaint alleges that the MGPs generated hazardous wastes, that PG & E contributed to the handling of that waste, and that this waste presents an imminent and substantial danger to the environment&emdash;namely, the Bay and the herring population. It provides facts to support each of these assertions. Therefore, the complaint adequately states a claim for relief under Rule 12(b)(6). Although the defendants argue that SFHA has not requested any relief with respect to its RCRA claim, see Mot. 22-23, this is not true. As with the CWA claim, the plaintiffs request an injunction and other damages. See Compl. at 65.
Second, PG & E argues that regulatory oversight of the remediation efforts renders SFHA’s RCRA claim moot. Mot. 8-9. However, it does not provide any other information to support this argument. As with Clarke’s claim under the RCRA, the complaint provides that the oversight of current remediation efforts is inadequate. Compl. ¶¶ 165-207. Therefore, a question of fact exists regarding the remediation efforts, and the RCRA claim is not moot.
Finally, the defendants argue that SFHA’s RCRA claims are precluded by the analogous provisions of the CWA. Reply 4. The statute directs the EPA Administrator to “avoid duplication, to the maximum extent practicable” between RCRA regulation and government regulation under CWA and other environmental acts. 42 U.S.C. § 6905(b). It provides that “[s]uch integration shall be effected only to the extent that it can be done in a manner consistent with the goals and policies expressed in this chapter and in the other acts referred to in this subsection.” Id.
Courts have come to differing conclusions regarding the propriety of granting a motion to dismiss based upon the anti-duplication provisions of the RCRA. In Sherrill v. Mayor & City Council of Balti
Other courts have declined to dispose of RCRA claims based upon section 6905 at the motion to dismiss stage because “discovery is needed to determine if the RCRA and CWA are inconsistent.” Raritan Baykeeper, Inc. v. NL Indus., Inc., No. 09-CV-4117 JAP;
Raritan Baykeeper is pertinent to this case. There, the court stated: “[w]hen two statutes are capáble of co-existence, it is the duty of the courts, absent a clearly expressed congressional intention to the contrary, to regard each as effective. When there are two acts upon the same subject, the rule is to give effect to both if possible.... Defendants have the burden to show that ... an inconsistency would result.”
CONCLUSION
For the above reasons, I DENY PG & E’s motion to dismiss. PG & E shall file an answer within twenty days from the date of this order.
IT IS SO ORDERED.
Notes
. Photo-enhanced toxicity, also known as phototoxicity, leads to long-term weakening of the swimming capacity of the fish that do survive exposure to PAHs. Compl. ¶ 99.
. I GRANT the defendants’ request for judicial notice of the NOI, as it is a matter of public record. See Jamul Action Comm. v. Stevens, No. 2:13-CV-01920-KJM,
. I note that whether migrating contaminants can constitute an ongoing violation when an unlawful activity has ceased is a question that has divided courts. See Sierra Club v. El Paso Gold Mines, Inc.,
. It is worth noting that these cases, and others with similar holdings, addressed the issue of imminent and substantial danger and any offset of remediation efforts on summary judgment.
. PG & E cites to Price v. U.S. Navy,
.The plaintiffs argue that the defendants improperly moved to dismiss this portion of the complaint pursuant to Rule 12(b)(6), when they should have moved to strike under Rule 12(f). They request leave to file a response if the court treats the defendants' argument as a motion to strike. Because I find that it is improper to dismiss or strike this portion of ■ the complaint, the plaintiffs’ request is denied as moot.
