² The Livaudais properties “consist of three unconnected parcels of land in the northwestern corner of the MRGO,” Parcel A, Parcel B, and Parcel C. 2017 Mendelssohn Report at 36. “Parcel A, the northwesterly parcel, is a narrow but long 109 ac. rectangle with organic solid of the Lafitte soil series, typical of brackish marshes, within the marsh proper, and mineral dredged soils . . . in the MRGO dredge habitat . . . and [is] contiguous with the Jackson Protection Levee.” Id. at 36–37. “Parcel B, . . . [is] adjacent to the Mississippi River levee fastlands, is much wider than Parcel A, but shorter and consists of 312 ac. of mineral Barbary clays.” “Parcel C, . . . is the longest of the parcels, but narrow, and consists of 386 ac. of both organic soils . . . and mineral soils.” Id. 3 The Vincent property “covers about 6,800 acres in Orleans and St. Bernard Parishes . . . [where] the southern 40 percent of the property is located in the Central Wetlands.” Gov. Mot. for Summ. Judgment Ex. 37, ECF No. 99 at 3 (The Kemp Expert Report). 4 “The property of Borgnemouth Realty Company consists of two contiguous sections,” the Southeast and Northwest sections. 2017 Mendelssohn Report at 36. The Borgnemouth properties are in the Central Wetlands “that extend from the Mississippi River Levee in a northeast direction to Lake Borgne,” with portions of each property extending across the MRGO to the east. Id. at 30. “The Borgnemouth property, which includes a major portion of Proctor Point . . . [and] the soils of the Borgnemouth brackish and salt marshes are primarily organic . . . consisting of Clovelly and Lafitte muck.” Id. 5 Lake Eugenie, which has two separate property areas, the East and West, has a 240-acre area in the west located in the central wetlands, Eugenie West. Id. at 16. “The majority of the Lake Eugenie Land & Development . . . property is located along the outer fringe remnants of the St. Bernard delta, often referred to as the Biloxi marshes,” or Eugenie East. Id. Category One thus only includes Eugenie West. - 18 - MRGO construction ended in 1968, and the environmental effects of the MRGO on the surrounding marshlands began to occur soon after.6 See Gov. Mot. for Summ. J., Ex. 19 at 86– 88 (Environmental Baseline Study for the St. Bernard Parish Police Jury). A 1982 study found between 1955 and 1978, the Central Wetlands had lost all fresh-to-intermediate marsh, more than doubled the amount of brackish marsh, and introduced a significant amount of saline marsh.7 A further study published in 1982 described the environmental impact of saltwater intrusion and erosion as contributing to the loss of marshland in the immediate area. Gov. Mot. for Summ. J., Ex. 18 at 15–30 (St. Bernard Parish: A Study in Wetland Management). By 1984, the Corps released a report which noted the marshland around the St. Bernard Parish was disappearing at a rate of approximately 21,900 acres per year. See 1984 Initial Evaluation Study at 60–61. In 1986, Congress formally recognized problems surrounding the destruction of marshland by passing WRDA, establishing the Office of Environmental Policy to: [D]evelop, and monitor compliance with, guidelines for the consideration of environmental quality in formulation and planning of water resources projects carried out by the Secretary, the preparation and coordination of environmental impact statements for such projects, and the coordination with Federal, State, and local agencies of environmental aspects of such projects and regulatory responsibilities of the Secretary. 33 U.S.C. § 2294. In 1988, the Corps released a reconnaissance report which placed the previous reports of erosion and the MRGO into perspective: “Erosion and disintegration of the banks of the MR- GO has created many additional routes for saltwater to intrude into formerly less saline interior marshes. Consequently, salinity in the marshes has increased significantly in the last 20 years.” 1988 Reconnaissance Report at 27. The 1988 Reconnaissance Report found the increased salinity levels contributed to the reduction in “the amount of three-cornered grass” growing in the local marshlands, as well as the reduction of wildlife populations and vegetation in the marshland. Id. The Report thus concluded “[s]altwater intrusion . . . contributes significantly to marsh loss in the study area.” Id. Consistent with this date, the government points to 1988 and the release of the Corps Reconnaissance Report as the date plaintiffs’ claims “stabilized,” starting the statute of limitations. Gov. Mot. for Summ. J. at 36–37. Before constructing the MRGO, “[t]he United States obtained [from plaintiffs] federal navigational servitudes in the designed footprint of the channel, and also acquired rights of entry for construction and spoil disposal that extended 1500 feet from the channel’s original centerline.” Gov. Mot. for Summ. J. at 9. The marshland in close proximity to the channel creates a difficult question of fact as to whether any applicable government easement or servitude extends to takings occurring on those properties, particularly in attempting to 6 “Greater than 12,000 acres of the swamps in the CWU, South Lake Borgne and other units were killed shortly after the opening of the MRGO . . . .” Day Report at 19. “Levels of salinity in the Central Wetlands Unit . . . and adjacent areas . . . before the opening of the MRGO were generally between fresh and 4 ppt. After the MRGO was opened, salinities in the Central Wetlands Unit . . . were consistently higher than 5 ppt and often higher than 10 ppt.” Id. at 41–42. 7 During this period, the Central Wetlands lost all 5,678 acres of fresh-to-intermediate marsh, increased the number of acres of brackish marsh from 3,721 to 7,425, and added 1,198 acres of saline marsh. See Day Report at 48. - 19 - determine whether saltwater permeated beyond the bounds of the easement. As discussed in the Day Report, no two hydrological surveys of the area “necessarily exactly match those estimated by a different team” because “[d]iscrepancies may arise from interpretation techniques, sampling resolution, or differences in environmental factors.” Gov. Mot. for Summ. J., Ex. 8 (“Day Report”) at 37. Based on difficulties stemming from “the realities of the terrain and the difficulty in determining the exact boundary of the easement . . . requiring the plaintiffs to sue immediately upon initial encroachment . . . is too rigid of an application of the stabilization doctrine.” Boling, 220 F.3d at 1372–73. As the Court observed during its site visit and photographic exhibits in the record, the terrain of plaintiffs’ properties consists of vast amounts of irregular wetlands and marshes. See, e.g., Gov. Mot. for Summ. J., Ex. 11 at 2 (“Britsch Report”). This is especially the case where plaintiffs’ claim saltwater intrusion caused vegetation loss and in turn erosion, an occurrence not bound by specific geographical boundaries. See Boling, 220 F.3d 1373 (directing courts examining the stabilization doctrine to consider “the uncertainties of the terrain, the difficulty in determining the location of the government’s easement, and the irregular process of erosion”). These geographical features make it difficult to determine exact boundary lines and specific points where saltwater intrusion first permeated into properties and vegetation loss which may have led to the alleged land taking. Uncertainties of terrain and the irregularity of erosion left plaintiffs unable to immediately determine the permanency of any alleged taking following completion of the MRGO in 1968. As of at least 1982, Congress was still commissioning reports to determine the extent of erosion occurring in the areas around the MRGO. See 1988 Reconnaissance Report at 2. Plaintiffs’ claims may have stabilized as early as 1978, however, when local interests began the Violet Siphon program to provide freshwater diversions to Category One. See Fallini v. United States, 56 F.3d 1378, 1382 (Fed. Cir. 1995) (noting “[i]t is not necessary that the damages from the alleged taking be complete and fully calculable before the cause of action accrues . . . [so long as] the ‘permanent nature’ of the taking was evident”). The Violet Siphon program was a freshwater diversion system with the “objective of restoring the project area to a fresher state through mimicking the former behavior of the Mississippi River by siphoning fresh water into the marsh.” Pls.’ Mot. for Partial Summ. J., Ex. 46 at 1-14 (U.S. Army Corp. of Engineers “Final Environmental Impact Statement for the Mississippi River-Gulf Outlet (MRGO), Louisiana, and Lake Borgne – Wetland Creation and Shoreline Protection Project”). Planning the construction of the siphon may indicate local landowners were aware of the “substantial encroachment” of saltwater onto their property and affirmatively sought to counteract this encroachment with freshwater diversions to regain marshland. See Boling, 220 F.3d at 1372 (the stabilization doctrine requires the Court to determine when there was sufficient “substantial encroachment” onto plaintiffs’ land to make plaintiffs aware of the alleged taking). Plaintiffs argue the “gradual physical process that have eroded and continue to erode plaintiffs’ properties” either “to this date have not yet stabilized” or, if the claims have stabilized, “stabilization did not occur until July 9, 2009, when the MRGO was finally physically closed . . . .” Pls.’ Mot. for Partial Summ. J., at 2. At the time the 1988 Reconnaissance Report was released, however, landowners were not only made aware of the negative effects of saltwater intrusion by the Corps itself, but also were visually aware—or should have been visually aware—a taking was occurring. Plaintiffs’ claims in Category One are based on the theory saltwater intrusion killed the natural vegetation in the area, and erosion occurred when the roots - 20 - of these dead plants could no longer hold the soil in place. Am. Compl. at ¶ 31. The 1988 Reconnaissance Report explicitly highlights the increasing salinity of the marshes due to saltwater intrusion and corresponding loss of marshland, noting “salinity in the marshes has increased significantly in the last 20 years” which in turn “greatly reduced” marshland vegetation less tolerant to high salinity conditions. Pls.’ Mot. for Partial Summ. J., Ex. 7 at 27 (1988 Reconnaissance Report). By 1988, the increased salinity described in the 1988 Reconnaissance Report would likely have caused the same alleged physical ramifications as forms the basis for plaintiffs’ claims for erosion-based takings in Category One, namely the death of various plant life and conversion of the marshland from lower to higher-salinity marshes. A 1999 study further reinforces the permanency of the alleged taking around 1988, based on reports of hydrological effects occurring at the time.8 Stabilization does not require “the progressive environmental damage [to] stop[],” and the publishing of the 1988 Reconnaissance Report both publicly represented the government’s recognition of the issue of erosion caused by the MRGO and documented physical evidence of the substantial encroachment of saltwater onto plaintiffs’ land and the corresponding effects of this encroachment. Boling, 220 F.3d at 1371. By 1988, the saltwater plaintiffs attribute as the cause of erosion on their land sufficiently “invaded the private property such that the permanent nature of the taking is evident and the extent of the damage is reasonably foreseeable.” Id. In summary, for Category One, the evidence in the record indicates “environmental forces . . . substantially and permanently invaded the private property” sufficient for the stabilization doctrine to apply at some point between 1978, the year the Violet Siphon project was initiated, and 1988, the year the 1988 Reconnaissance Report was published. Boling, 220 F.3d at 1371. Viewing the evidence in the light most favorable to plaintiffs, however, stabilization of plaintiffs’ claims occurred in 1988 following the 1988 Reconnaissance Report and the visible physical changes occurring on the property. On the other hand, viewing the evidence in the light most favorable to the government, stabilization of plaintiffs’ claims occurred when local interests recognized the potential permanency of erosion in Category One and initiated the Violet Siphon program as an attempt to counteract the erosion. See Matsushita Elec. Indus. Co., Ltd. v. Zenith Radio Corp., 475 U.S. 574, 587–88 (1986) (noting courts must draw all inferences at the summary judgment stage “in the light most favorable to the party opposing the motion”). Therefore, for the purpose of the government’s motion for summary judgment, absent justifiable uncertainty tolling the statute of limitations, the six-year statute of limitations period for plaintiffs’ claims in Category One expired in 1994. For the purpose of plaintiffs’ motion for summary judgment, absent justifiable uncertainty tolling the statute of limitations, the six-year statute of limitations period for plaintiffs’ claims in Category One expired in 1984. See Applegate v. United States, 25 F.3d 1579, 1583 (Fed. Cir. 1994). B. Justifiable Uncertainty For landowners to be “justifiably uncertain” as to the permanency of the alleged taking, “the question is whether the ‘predictability [and permanence] of the extent of damage to the 8 Between 1956 and 1978, the amount of fresh-to-intermediate marsh decreased from 11,620 acres to 1,520 acres, while the amount of brackish marsh increased from 13,490 acres to 21,710 acres. From 1978 to 1990, however, the amount of fresh-to-intermediate marsh decreased only from 1,520 acres to 620 acres, and the amount of brackish marsh actually decreased from 21,710 acres to 19,710 acres. See Day Report at 53. - 21 - [plaintiffs’] land’ was made justifiably uncertain by the Corps’ mitigation efforts.” Banks v. United States. 314 F.3d 1304, 1309 (Fed. Cir. 2003) (citing Applegate, 25 F.3d at 1583). A project aimed at mitigating damages would constitute justifiable uncertainty as to the permanency of the alleged taking, thus tolling the statute of limitations, if it were implemented after the date on which the Court deems plaintiffs alleged taking to have “stabilized.” Banks, 314 F.3d at 1309. To determine whether proposed or actual mitigation efforts by the Corps made landowners justifiably uncertain as to the permanency of the alleged takings in Category One and therefore tolled the statute of limitations, the Court twice ordered plaintiffs to provide supplemental briefing listing proposed and completed projects affecting the justifiable uncertainty analysis of Category One, and the government had an opportunity to respond to each. See Order, ECF No. 152; Order, ECF No. 160. All projects plaintiffs provided as applicable to the justifiable uncertainty analysis are considered in the Court’s analysis.9 As early as 1979, the local interests began taking steps to mitigate damage to marshlands in the Central Wetlands by building the Violet Siphon to revitalize the area through delivery of fresh water.10 See Day Report at 29. The Violet Siphon program was initiated in 1978, the siphon was built by the St. Bernard Parish in 1979, and it initially operated until 1983. Id. The Violet Siphon “was again brought into operation [by the Louisiana Department of Natural Resources] . . . beginning in 1990.” Id. The Violet Siphon “was operated for four years in the mid-1990s . . . and was not maintained subsequent to 1997 . . . .” Gov. Mot. Summ. J., Ex. 16 at 42 (Assessment of Wetland Habitat Change on Litigated Properties Adjacent to The Mississippi River Gulf Outlet (MRGO)) (“2017 Mendelssohn Report”). And in 2003, repairs were made to rehabilitate the Violet [S]iphon . . . and the siphon was reopened shortly after the repairs were made.11 Id. The Violet Siphon “was intended to freshen 17,980 acres of cypress swamp and marsh near the outfall into the Central Wetlands.” Id.12 Plaintiffs argue “[t]he Violet Siphons 9 Plaintiffs’ 15 June 2020 supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category One: The Louisiana Coastal Wetlands Restoration of 1993; the Mississippi River Gulf Outlet Ecosystem Restoration Plan’s Final Feasibility Report; and the beneficial use of dredged materials. See Pls.’ Paper at 1–2. Plaintiffs’ 30 June 2020 supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category One: the “Violet Siphon” freshwater diversion project; the Coastal Wetlands Planning, Protection, and Restoration Act and related wetlands construction projects proposed, planned, or funded under the Act; the establishment of the Coastal Wetlands Planning, Protection, and Restoration Act Task Force’s Coast 2050 Report; the Water Resources Development Act and related wetlands construction projects proposed, planned, or funded under the Act, the Mississippi River-Gulf Outlet Ecosystem Restoration Plan and related wetlands construction projects proposed, planned, or funded under the plan; and the Mendelssohn Report. See Pls.’ Supp. Paper at 2–15. 10 “The Violet Siphons were constructed with the objective of restoring the project area to a fresher state through mimicking the former behavior of the Mississippi River by siphoning fresh water into the marsh. The siphons were operational for only four years due primarily to public opposition to large amounts of sediment deposited in [the] Violet Canal, interfering with navigation.” Pls.’ Mot. for Partial Summ. J., Ex. 46 at 1–14 (U.S. Army Corp. of Engineers “Final Environmental Impact Statement for the Mississippi River-Gulf Outlet (MRGO), Louisiana, and Lake Borgne – Wetland Creation and Shoreline Protection Project”). 11 The Violet Siphon was put back into operation after the Louisiana Department of Natural Resources completed the Violet Siphon Diversion project, which “return[ed] into operation the existing siphon, and [] enlarge[d] the size of the diversion so that more sediment and freshwater are available to offset marsh subsidence and saltwater intrusion.” Pls.’ Supp. Paper at 4. 12 As stated in the Mendelssohn Report, when discussing saltwater intrusion during 2001 to 2013, “the salt marsh in the southern portion of [the Borgnemouth Property] began to retreat in 2009 in the direction from which it had expanded, completely disappearing in 2007 and 2013 . . . . It is plausible that freshwater discharge from the Violet - 22 - were constructed with the objective of restoring the project area to a fresher state” and provided sediment and freshwater “to offset marsh subsidence and saltwater intrusion.” See Pls.’ Supp. Paper at 3–4 (citations omitted). The government argues in response, “[u]nlike the projects in Applegate and Banks,” the Violet Siphon “was not conceived to ‘mitigate’ the effects of the Corps’ Mississippi River Gulf Outlet,” and “[p]laintiffs offer no evidence that the locally-built Violet Siphon had any impact on freshening the vegetation or remediating land loss on their properties between 1979 and 1983.”13 Gov.’s Resp. to Pls.’ Supp. Paper at 3–4. A landowner need not receive “a legally binding promise or duty or a matter requiring a congressional appropriation” to be justifiably uncertain as to the permanency of an alleged taking. Banks, 314 F.3d at 1309. Rather, the “mere promise” of mitigation efforts, “held out by the Corps and repeatedly renewed but never implemented, indicate[s] that ‘the landowners did not know when or if their land would be permanently destroyed.’” Id. (quoting Applegate, 25 F.3d at 1583). “[P]roposals to correct the damage” done to the land put forward by the government can “further complicate[] ascertaining the extent and nature of the consequences” of the physical taking enough to trigger the doctrine of justifiable uncertainty. Applegate, 25 F.3d at 1584. Throughout the early 1990s, the Corps began to move forward with additional plans, task forces, and completed projects directed to the goal of “no overall net loss of the Nation’s remaining wetlands base . . . .” 1990 WRDA at § 307(a).14 By the late 1990s, and stretching Canal played a role in the freshening of the southern portion of [the Borgnemouth Property] from 2001 through 2013.” 2017 Mendelssohn Report at 35. 13 The government argues justifiable uncertainty requires “objectively reasonable beliefs that the United States would completely reverse and remediate government-caused erosion” and, because the Violet Siphon was “first built ‘by local interests,’” and “not a federal project,” the Court should not consider the Violet Siphon in any justifiable uncertainty analysis before it “was rebuilt as a State project in 1992 . . . .” Gov.’s Response to Pls.’ Supp. Paper at 2–4. As the Court assumes the stabilization date for the purposes of the government’s motion for summary judgment is 1988, it need not decide at this time whether the “first operation” of the Violet Siphon constituted justifiable uncertainty. The government admits the Violet Siphon was rebuilt in 1992, and therefore its operation as a “state project” began within the statute of limitations period running from 1988. To the extent the original operation of the Violet Siphon by “local interests” affects whether landowners were justifiably uncertain as to the permanency of the alleged takings in Category One, projects to restore damaged land conducted by entities besides the government may still leave a landowner justifiably uncertain as to the permanency of any alleged government taking. The government’s promise in Applegate to restore the littoral flow was specifically what “destroyed any predictability of the extent of damage to the land,” but the ultimate question the Federal Circuit emphasized as determining whether landowners were justifiably uncertain was whether the landowners knew “when or if their land would be permanently destroyed.” Applegate, 25 F.3d at 1582–83; see also Banks, 314 F.3d at 1309 (“This court has noted that the ‘critical element that delayed stabilization in Applegate [is] the justifiable uncertainty about the permanency of the taking.’”) (quoting Boling, 220 F.3d at 1372) (citations omitted). Further, at this stage the record is not clear as to the source of funding for the initial operation of the Violet Siphon or whether the initial operation was supported by federal money. 14 In 1990, Congress passed the Water Resource Development Act of 1990. See the 1990 WRDA. Additional legislation in 1990 included the Coastal Wetlands Planning, Protection and Restoration Act directed the Corps to establish a comprehensive plan to restore Louisiana wetlands and called for the development of annual lists of “priority projects,” which would “provide for the long-term conservation of [Louisiana’s] wetlands . . . .” Pls.’ Mot. for Partial Summ., Ex. 42 at 3–4 (1994 MRGO Bank Erosion Reconnaissance Report). In 1993, a task force submitted a plan to restore and prevent further loss in Louisiana wetlands by “increas[ing] sediment and freshwater input into coastal estuaries” so as to “restart the natural processes of land building and maintenance . . . .” Pls.’ Mot. for Partial Summ. J., Ex. 41 at 9 (1993 Louisiana Coastal Wetlands Restoration Plan). The task force behind the 1993 Louisiana Coastal Wetlands Restoration Plan developed a “comprehensive approach to restore and prevent the loss of coastal wetlands in Louisiana” by using hydrologic restoration, shoreline protection, marsh creation with dredged materials, and marsh management. Id. at 9, 24. - 23 - into the early 2000s, the Corps continued planning and implementing additional projects15 to further mitigate any alleged negative effects to the marshlands.16 Following Hurricane Katrina in 2005, additional projects were contemplated and implemented which effected the marshland areas in the Central Wetlands.17 The marshlands of the Central Wetlands region experienced significant fluctuations in salinity classifications during the time period overlapping with the various projects performed and proposed by the Corps.18 Between 1988 and 1997, certain areas of marshland cycled 15 In 1994, the Corps prepared a bank erosion reconnaissance report, which studied projects approved in the 1991, 1992, and 1993 reports, including the “Violet Freshwater Distribution project” which aimed to “increase the use of fresh water, nutrients, and sediments drawn from the Mississippi River from the existing Violet Siphon.” Pls.’ Mot. for Partial Summ. J., Ex. 42 at 4. This project was reauthorized under the 2007 WRDA. Pls.’ Mot. for Partial Summ. J., Ex. 46 at 1–14 (U.S. Army Corp. of Engineers “Final Environmental Impact Statement for the Mississippi River-Gulf Outlet (MRGO), Louisiana, and Lake Borgne – Wetland Creation and Shoreline Protection Project”). 16 In 1999, under the 1996 WRDA, the Corps conducted three projects along the MRGO to create 76 acres of wetlands with materials dredged from the channel. Am. Compl. at ¶ 31. In the 2004 USCAE LCA Ecosystem Restoration study, the Corps warned that the “rate of wetland loss in the area is accelerating” and “[r]apid action is required to protect the integrity of the southern Lake Borgne shoreline and to prevent continued erosion of the MRGO channel banks from ocean going vessel wakes.” Pls.’ Mot. for Partial Summ. J., Ex. 45 at 31 (U.S. Army Corps of Engineers, Louisiana Coastal Area (LCA), Louisiana, Ecosystem Restoration Study (November 2004)). The Corps proposed building 38 miles of rock breakwaters along the banks of the MRGO to prevent the merger of the MRGO and Lake Borgne, noting such construction “has been effectively used . . . to prevent bankline retreat and protect large areas of estuarine wetlands from further erosion and degradation.” Id. at 2. The rock breakwaters further “may also facilitate future wetland creation using dedicated dredging and/or beneficial use of dredged material . . . .” Id. at 32. Additionally, in 2004, the Corps presented in a PowerPoint demonstration the Breaux Act Projects, which detailed four projects at the preliminary engineering design (“PED”) phase and two projects constructed. Pls.’ Reply Br. Opp’n, Ex. 56 at 46–47 (U.S. Army Corps of Engineers, MRGO Studies). The PED projects included two shoreline protection projects along Lake Borgne and the MRGO with an estimated cost of $45 million to benefit 495 acres of land, and the constructed projects included two hydrologic restoration projects in the same area which cost $2.6 million and benefited 889 acres. Id. 17 In 2006, Congress mandated the Corps develop a comprehensive plan to de-authorize the MRGO, and in the 2007 WRDA, Congress authorized the closure of the MRGO. Pls.’ Mot. for Partial Summ. J., Ex. 51 at 1 (Mississippi River-Gulf Outlet Deep Draft De-authorization Study). The WRDA authorized and appropriated projects including: placing 23 miles of rock break along the north bank, adding 15 miles of rock break along the southern shore of Lake Borgne, and addressing the loss of 6,350 acres of marsh. Pls.’ Mot. for Partial Summ. J., Ex. 46 at 1-12 (U.S. Army Corp. of Engineers “Final Environmental Impact Statement for the Mississippi River-Gulf Outlet (MRGO), Louisiana, and Lake Borgne – Wetland Creation and Shoreline Protection Project”). In June 2009, the USCAE prepared the Final Environmental Impact Statement for MRGO-Wetland Creation and Shoreline Protection Project, which proposed “construct[ing] shoreline protection features along the Lake Borgne shoreline and restore and nourish wetlands in the MRGO and Lake Borgne estuarine complex.” Pls.’ Mot. for Partial Summ. J., Ex. 46 at ES- 1 (U.S. Army Corp. of Engineers “Final Environmental Impact Statement for the Mississippi River-Gulf Outlet (MRGO), Louisiana, and Lake Borgne – Wetland Creation and Shoreline Protection Project”). The funding for these projects was envisioned to come from $75,000,000 Congress appropriated “for the repair, construction or provision of measures or structures necessary to protect, restore or increase wetlands, to prevent saltwater intrusion or storm surge.” Id. at ES-2. In July 2009, the Corps officially closed the MRGO, and no non-federal sponsor came forward to begin the authorized restoration projects, delaying restoration efforts. See 2012 Feasibility Report at S-2. In June 2012, the Corps prepared the Mississippi River Gulf Outlet Ecosystem and Restoration Plan Final Feasibility Report with the purpose “to develop alternative plans to restore natural features and processes in the Lake Borgne ecosystem and areas affected by the former navigation channel.” Id. at S-6. 18 “In the Central Wetlands, there was no fresh marsh. Intermediate marsh has decreased significantly (2,814 acres) and brackish marsh had increased (14,628 acres). Swamp decrease significantly (1,817 acres) and occurred only where there was a dependable source of fresh water such as around pumping stations that introduced water from rainfall and treated municipal effluent.” Day Report at 45. “In the Central Wetlands Unit, from the 1950s to the - 24 - between classification as brackish marsh, intermediate marsh, and saline marsh.19 In other areas of the marshlands of the Central Wetlands, similar fluctuations in the levels of brackish and salt marshes occurred between 1968 and 2013.20 An additional area of marshland in the Central Wetlands observed similar oscillation in the level of brackish marsh between 1968 and 2013.21 Lastly, a final area of marshland also experienced significant fluctuation in levels of brackish marsh between 1968 and 2013.22 Fluctuations in the salinity of the Category One marshlands are significant because plaintiffs’ theory of takings is based on saltwater intrusion increasing the salinity of the marshland, which allegedly killed the natural vegetation of the marsh and led to erosion of soil no longer held in place by root systems. Am. Compl. at ¶ 31. A decrease in the salinity of Category One could indicate to landowners the Violet Siphon is both effectively providing sediment dispersals through freshwater diversions and is lowering the salinity of the surrounding marshlands enough to drastically slow the rate of erosion.23 A landowner reading reports on the planned restoration of the marsh through freshwater diversion and observing the fluctuations in salinity could therefore reasonably assume the Corps projects are mitigating any negative effects of the MRGO to the wetlands. Applegate, 25 F.3d at 1584 (finding “[t]he Corps 2000s, there were decreases in fresh marsh (-11,120 acres) and swamp (-7,812 acres) . . . . There were increases in intermediate (2,814 acres) and brackish (1,175) marsh, open water (5,239 acres) and spoil (9,315) acres.” Id. at 46. 19 “[H]abitat change was considerable between 1988 and 1997. Brackish marsh decreased from 61.5% of the property to 33% due primarily to conversion to saline marsh, which comprised 15% of the property. The increase in water habitat (32.5% of the property) appears to have resulted from both interior pond formation and from erosion along the MRGO. Intermediate marsh habitat comprised 7% of the property, most likely arising from the freshening effect of the violet siphon.” 2018 Mendelssohn Report at 4. Yet just four years later, in 2001, “saline marsh had converted back to brackish marsh, covering 49% of the property, with little intermediate marsh (0.5%) and water comprising 39% of the property.” Id. 20 The level of brackish marsh steadily increased in Eugenie West by one acre from 1968 to 1978, from 1978 to 1988, and from 1988 to 1997. From 1997 on, however, the area of brackish marsh steadily fell by at least one acre from 1997 to 2001, from 2001 to 2007, and from 2007 to 2013. 2017 Mendelssohn Report at 52. For the Borgnemouth property, the level of brackish marsh steadily increased up until sometime between 1978 and 1988; whereupon a sharp drop in the acreage of brackish marsh was experienced until a point in time between 1997 and 2001. Id. at 54. At some point between 2001 and 2007, however, the level of brackish marsh again dropped and stayed at this lower level until the study concluded in 2013. Id. The acreage of salt marsh on the Borgnemouth property also underwent significant fluctuation. Following construction of the MRGO, all salt marsh disappeared sometime between 1978 and 1988. By 1988, however, a significant area of land (1,283 acres) became salt marsh. This level steadily dropped until ultimately reaching zero again by 2007, only to increase again by 2013 to more than 700 acres. Id. 21 The level of brackish marsh for the Livaudais properties steadily increased following construction of the MRGO until somewhere between 1978 and 1988. Thereafter, a decrease in the level of brackish marsh was observed until somewhere between 1997 and 2001, where a large spike of more than 400 acres of brackish marsh reappeared. Thereafter, the levels of brackish marsh began gradually decreasing. See 2017 Mendelssohn Report at 55. 22 In the Vincent Marshlands, the levels of brackish marsh steadily decreased from 1968 to 1997. From 1997 to 2001, however, the levels of brackish marsh increased by nearly 1,500 acres. From 2001 to 2013, the levels of brackish marsh began to fall again, though still remaining nearly 1,000 acres larger than their lowest recorded level in 1997. See 2018 Mendelssohn Report at 57. 23 The first operation of the Violet Siphon was shut down because it was depositing sediment in the Violet Canal so effectively it was interfering with navigation along the canal. Pls’ Mot. for Partial Summ. J. Ex. 46 at 1–14 (U.S. Army Corp. of Engineers “Final Environmental Impact Statement for the Mississippi River-Gulf Outlet (MRGO), Louisiana, and Lake Borgne – Wetland Creation and Shoreline Protection Project”). A landowner could reasonably believe the continued operation of the Violet Siphon would result in additional sediment being deposited into Category One, counteracting the effects of erosion on the surrounding area. - 25 - further complicated ascertaining the extent and nature of the consequences of this process with proposals to correct the damage”). The studies and project proposals on marshland restoration, combined with the previously completed projects in the marshlands of the Central Wetlands and the fluctuations in salinity of the Central Wetlands during the period in time the government completed restoration projects, demonstrate the government’s commitment to mitigation efforts. The actual and proposed mitigation activities affecting Category One may contribute to when “a land owner should have known the land suffered erosion,” because the government’s actual or proposed mitigation created “greater uncertainty . . . [when] the Corps in this case actually performed its mitigation activities.” Boling, 220 F.3d at 1373; Banks at 1309–10. A landowner could reasonably rely on previously completed projects in the marshlands, such as intermittent operation of the Violet Siphon, in addition to public reports and grants related to future projects, to provide redress for the accrued damage from erosion. In particular, the Violet Siphon acted to provide an outflow of fresh water into the marshlands of Category One “so that more sediment and freshwater are available to offset marsh subsidence and saltwater intrusion.” Pls.’ Supp. Paper at 4. Although the completion of the MRGO had an immediate effect on the surrounding marshlands, the uncertainties of terrain, difficulties in determining the location of the government’s easement, and irregularity of the erosion meant plaintiffs’ claims did not stabilize immediately upon the channel’s opening but rather likely stabilized at some point between 1978 and 1988. Viewing the evidence in the light most favorable to plaintiffs, stabilization of plaintiffs’ takings claims in Category One occurred by 1988, when the 1988 Reconnaissance Report was published and the physical changes should have been apparent. For the purposes of the cross-motions for summary judgment, the Court therefore concludes the evidence before it indicates stabilization occurred no later than 1988. The Violet Siphon, which was constructed in 1979 and was operated intermittently throughout the 1980s, 1990s, and 2000s, was specifically constructed with the objective of “restoring the project area to a fresher state through mimicking the former behavior of the Mississippi River by siphoning fresh water into the marsh.” Pls.’ Mot. for Partial Summ. J., Ex. 46 at 1-14 (U.S. Army Corp. of Engineers “Final Environmental Impact Statement for the Mississippi River-Gulf Outlet (MRGO), Louisiana, and Lake Borgne – Wetland Creation and Shoreline Protection Project”). Furthermore, plaintiffs cite various planned and completed beneficial dredging and wetland creation projects running through 2009 or later. Reading the evidence of the government’s proposed and completed mitigation efforts in the light most favorable to plaintiffs, justifiable uncertainty may toll the statute of limitations on plaintiffs’ claims related to Category One. Banks, 314 F.3d at 1310. VII. Analysis of Category Two – South Lake Borgne South Lake Borgne corresponds to geographical “Subunit 40” of Exhibit 1 contained in the 2012 Feasibility Report. 2012 Feasibility Report at 2-58. Subunit 40 includes the - 26 - Livaudais,24 Vincent Marshlands,25 Borgnemouth,26 Biloxi,27 and Lake Eugenie properties.28 See JSR at 1. “South Lake Borgne covers the MRGO/Lake Borgne Landbridge, the strip of marsh separating the MRGO from the [L]ake [Borgne].” 2012 Feasibility Report at 2-122, Figure 2-29. South Lake Borgne is located on the north side of the MRGO adjacent to the Central Wetlands. Id. There are thus two distinct types of land within Category Two: property situated on the banks of the channel and the remaining marshlands. A. Channel Land Area 1. Stabilization Doctrine For land situated on the channel itself, plaintiffs allege the following physical taking: Because the soft soils on the sides of the original channel would not stand up at such a steep angle, and because of the maintenance . . . conducted by the Corps of Engineers, the soil began to slide or “slough-off” into the bottom of the channel. . . . [T]he erosion process has continued over the years up to this date, and as a result, the channel is now over 2,000 feet wide at the surface. . . . This erosion process will continue into the future unless additional and complete shore protection measures to prevent future erosion are immediately implemented . . . . Am. Compl. ¶ 30. The MRGO channel cut directly through South Lake Borgne, which was only open to Lake Borgne on its northern bank. In 1968, the MRGO’s initial surface width was 650 feet, with a bottom width of 500 feet. See Britsch Report at 41. Prior to construction of the MRGO, “[t]he United States obtained [from plaintiffs] federal navigational servitudes in the designed footprint of the channel, and also acquired rights of entry for construction and spoil disposal that extended 1500 feet from the channel’s original centerline.” Gov. Mot. for Summ. J. at 9. Beginning in at least 1983 and ranging through the 1980s, the government conducted Environmental Assessments (“EAs”) related to “foreshore protection test sections” along the bank of the MRGO touching Category Two.29 These EAs may have been a direct response by the government to the substantial changes to the width of the channel and issues related to 24 For Livaudais, Parcel C extends across the MRGO into South Lake Borgne. See 2017 Mendelssohn Report at 36– 37. 25 The Vincent Marshlands property is one continuous piece of property extending across the MRGO into South Lake Borgne. 2018 Mendelssohn Report at 25. 26 Both the Southeast and Northwest Borgnemouth properties extend across the MRGO into South Lake Borgne, with the Southeast property extending into proctor point. 2017 Mendelssohn Report at 56. 27 Biloxi owns two separate property groups, Biloxi East and Biloxi West. “The majority of the [Biloxi East] property . . . is located to the west of Lake Eugenie Land & Development property, but still within the Biloxi marshes.” Id. at 23. Biloxi West is “a smaller section of land at Proctor Point.” Id. “The [Biloxi West] property- section is characterized by organic brackish marsh soils of the Lafitte and Clovelly series. The Lafitte muck has a thicker organic layer than the Clovelly muck.” Id. at 24. 28 For Lake Eugenie, a portion of the Western property is in South Lake Borgne. Id. at 56. 29 See Pls.’ Paper at 3 (listing EA #38 as signed 15 August 1983 and affecting land in Category Two). - 27 - erosion occurring along the banks, indicating the government was aware of all of the facts necessary to stabilize a takings claim. See Fallini v. United States, 56 F.3d 1378, 1382 (Fed. Cir. 1995) (noting “[i]t is not necessary that the damages from the alleged taking be complete and fully calculable before the cause of action accrues . . . [so long as] the ‘permanent nature’ of the taking was evident”). Consequently, it may also therefore indicate landowners along the channel should have similarly been aware by this point of the stabilization of their takings claim. Id. In 1988, the Corps published the 1988 Reconnaissance Report, which stated the MRGO “land cut has increased from [a top width of] 650 feet to an average of 1,500 feet” and “the unleveed reaches are retreating at varying rates from five to over 40 feet per year.” 1988 Reconnaissance Report at 26, 30. Thus, while the government originally received servitudes extending up to 1,500 feet from the centerline of the channel for construction and spoil disposal, the entirety of the area granted in the servitudes was now being utilized only for the channel itself. Id. By 1988 the average width of the channel therefore exceeded the original channel footprint by more than 230%. Stabilization does not require “the progressive environmental damage [to] stop[]”; this nearly 1,000-foot increase in the width of the channel constitutes a substantial and permanent invasion of “private property such that the permanent nature of the taking is evident and the extent of the damage is reasonably foreseeable.” Boling v. United States, 220 F.3d 1365, 1371 (Fed. Cir. 2000); see also id. at 1373 (holding “the takings claims accrued when the erosion has substantially encroached the parcels at issue and the damages were reasonably foreseeable”). Landowners’ claims would have therefore stabilized by at least the time the 1988 Reconnaissance Report was released. The evidence available in the record related to bank erosion and the widening of the channel indicate there was “substantial and permanent” invasion of private property sufficient to trigger the stabilization doctrine at some point between 1983, when the government started issuing EAs potentially affecting the widening of the MRGO channel, and 1988, the year the 1988 Reconnaissance Report detailed the substantial widening of the channel. For the purpose of the government’s motion for summary judgment, by at least 1988 the dramatic growth of the channel and the release of the 1988 Reconnaissance Report put the landowners on adequate notice for a taking to accrue. Therefore, absent justifiable uncertainty tolling the statute of limitations, the six-year statute of limitations period for plaintiffs’ claims along the channel of Category Two expired in 1994. See Applegate v. United States, 25 F.3d 1579, 1583 (Fed. Cir. 1994). 2. Justifiable Uncertainty For landowners to be “justifiably uncertain” as to the permanency of the alleged taking, the “question is whether the ‘predictability [and permanence] of the extent of damage to the [plaintiffs’] land’ was made justifiably uncertain by the Corps’ mitigation efforts.” Banks v. United States, 314 F.3d 1304, 1309 (Fed. Cir. 2003) (citing Applegate, 25 F.3d at 1583). A project aimed at mitigating damages would constitute justifiable uncertainty as to the permanency of the alleged taking, thus tolling the statute of limitations, if it were implemented after the date on which the Court deems plaintiffs alleged the taking to have “stabilized.” Id. To determine whether proposed or actual mitigation efforts by the Corps made landowners justifiably uncertain as to the permanency of the alleged takings of land along the channel of Category Two and therefore tolled the statute of limitations, the Court twice ordered plaintiffs to - 28 - provide supplemental briefing listing proposed and completed projects affecting the justifiable uncertainty analysis of Category Two, and the government had an opportunity to respond to each. See Order, ECF No. 152; Order, ECF No. 160. All projects plaintiffs provided as applicable to the justifiable uncertainty analysis are considered in the Court’s analysis.30 From the period of 1988 to 2008, the Corps completed a series of projects constructing various forms of foreshore protections to address the environmental and physical impacts of the MRGO on property along the channel.31 These completed projects demonstrate the Corps’ commitment to the actual implementation of mitigation efforts to restore plaintiffs’ lands on or around the channel, and they create justifiable uncertainty with plaintiffs sufficient to toll the statute of limitations. Banks, 314 F.3d at 1309. 30 Plaintiffs’ 15 June supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category Two: Completed foreshore test construction projects; the “USACE Louisiana Coast Area Land Loss and Marsh Creation Initial Evaluation Study” and proposals for beneficial use of dredged materials contained therein; various reports related to bank and marshland erosion; the Louisiana Coastal Wetlands Restoration Plan of 1993; proposed or completed channel bank stabilization projects; and other proposed or completed projects related to the beneficial use of dredged materials. See Pls.’ Paper at 2–5. Plaintiffs’ 30 June supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category Two: Completed projects related to the “installation of foreshore protection and beneficial use of dredged material,” “various” completed CWPPRA projects, and “several” foreshore construction or remediation projects proposed but not completed. See Pls.’ Supp. Paper, at 30–31. 31 The 1988 Reconnaissance Report detailed “[f]oreshore protection along the north bank of the MR-GO . . . [was] completed.” 1988 Reconnaissance Report at 14. In 1991, EA #152 detailed a completed project where “[t]he purpose of the project [was] to stabilize the north bank of the MRGO channel between Mile 50.5 and Mile 55.0 while protecting adjacent marsh from further erosion.” Pls.’ Mot. for Partial Summ. J., Ex. 18 at 2 (EA #152: Bank Stabilization, Miles 50.5 to 55). In 1993, the Corps prepared an Issue Paper addressing bank erosion along the MRGO stating: “Using FY 1992 Congressional aid funds in the amount of $3.5 million, 3.5 miles of rock bank stabilization along the north bank of the channel have been constructed. Other measures to reduce erosion and restore marsh are being addressed in an ongoing reconnaissance study, Mississippi River-Gulf Outlet Bank Erosion, Louisiana, which is seeking the best plan, based on monetary and non-monetary benefits, to stabilize and restore the banks of the ship channel.” Pls.’ Mot. for Partial Summ. J., Ex. 11 at 1 (Issue Paper: Mississippi River-Gulf Outlet, LA- Bank Erosion). In 1996, EA #247 detailed a completed project where the purpose of the proposed action was to stabilize the left descending (north) bank of the MRGO channel, between Miles 55.0 and 56.1, while protecting adjacent marsh from further erosion. Pls.’ Mot. for Partial Summ. J., Ex. 23 at EA-4 (EA #247: Bank Stabilization, Miles 55.0 to 56.1). In 1999, the Corps detailed in EA #288 the construction of a non-continuous rock bank along the north bank of the MRGO. See Pls.’ Mot. for Partial Summ. J., Ex. 29 at 1 (EA #288: Mile 43 to Mile 41 North Bank Stabilization). In 2004, EA #402 proposed a “14,360 linear foot rock breakwater . . . along the north bank” of the MRGO. Pls.’ Mot. for Partial Summ. J., Ex. 35 at 1 (EA #402: Lake Borgne-MRGO Shoreline Protection Project). In in 2005 civil action brought in the United States District Court Eastern District of Louisiana, plaintiffs in the case stipulated to the government’s “Proposed Findings of Fact and Conclusions of Law” that “foreshore protection had been installed along the 6 miles of the north bank and 18 miles of the south bank of the MRGO as of August 29, 2005.” Pls.’ Mot. for Partial Summ. J., Ex. 5 at 14 (United States of America’s Proposed Findings of Fact and Conclusions of Law in In Re: Katrina Canal Breaches Consolidated Litigation). In 2009, the Corps detailed in the 2009 Final Environmental Impact Statement for the MRGO how the United States Environmental Protection Agency, in project number PO-30 for CWWPRA, “provided an overview of the impacts and/or benefits resulting from the installation of foreshore protection features in Lake Borgne. The goal of this project was to help preserve the existing wetland land bridge between Lake Borgne and the MRGO by constructing shoreline protection features along a total of 5.3 miles . . . of the Lake Borgne shoreline . . . [and] [t]his project was authorized for construction on February 8, 2006, and construction activities began in September 2007” and “completed in December 2008.” Pls.’ Mot. for Partial Summ. J., Ex. 46 at 1-11 (U.S. Army Corp. of Engineers “Final Environmental Impact Statement for the Mississippi River-Gulf Outlet (MRGO), Louisiana, and Lake Borgne – Wetland Creation and Shoreline Protection Project”). - 29 - Further, in addition to completed projects along the MRGO banks, plaintiff argues proposed projects contributed to landowners’ justifiable uncertainty. See Am. Compl. at ¶ 48– 56. A landowner need not receive “a legally binding promise or duty or a matter requiring a congressional appropriation” to be justifiably uncertain as to the permanency of an alleged taking. Banks, 314 F.3d at 1309. Rather, the “mere promise” of mitigation efforts, “held out by the Corps and repeatedly renewed but never implemented, indicate[s] that ‘the landowners did not know when or if their land would be permanently destroyed.’” Id. (quoting Applegate, 25 F.3d at 1583). “[P]roposals to correct the damage” done to the land put forward by the government can “further complicate[] ascertaining the extent and nature of the consequences” of the physical taking enough to trigger the doctrine of justifiable uncertainty. Applegate, 25 F.3d at 1584. Following the completed foreshore projects, numerous studies on the MRGO’s erosive effects, potential restoration plans, and projects proposed by the Corps were prepared with the intent to restore the MRGO to its pre-MRGO state with the support of legislation and the award of Congressional funds.32 Although some studies never received approval, others, including multiple renewals of the WRDA, received congressional funds and led to subsequent projects situated, at least in part, along the MRGO. Following Hurricane Katrina in 2005, additional projects were contemplated, and Congressional funds awarded, for restoration of the MRGO.33 Numerous studies contained specific projects aimed at restoring South Lake Borgne to preserve the land bridge separating Category Two from merging with Lake Borgne. While some of these studies did not focus specifically on South Lake Borgne itself, many of the studies concerned the entire channel, with detail regarding individual subunits—including South Lake Borgne. See Pls.’ Mot. for Partial Summ. J., Ex. 41 at 75–79; 2012 Feasibility Report at 2-57–2-62. Plaintiffs owning property situated on the channel itself could justifiably rely on those proposed restorative efforts affecting both their land specifically and those affecting the entire channel to conclude the 32 Throughout the early 1990s, the Corps began to move forward with additional plans, task forces, and completed projects directed to the goal of “no overall net loss of the Nation’s remaining wetlands base . . . .” See 1990 WRDA at § 307(a); see also supra at fn. 14. In 1994, the Corps published a reconnaissance report recommending both structural and nonstructural measures for “reducing bank erosion and/or restoring adjacent wetlands along the MR- GO. Structural measures included the construction of bank protection structures, such as rock dikes, along the channel; and the enlargement of the channel to increase its cross-sectional area.” Pls.’ Mot. for Partial Summ. J., Ex. 42 pt.1 at 35 (1994 MRGO Bank Erosion Reconnaissance Report). In 1998, a conglomerate of federal, state, and local governments published a report noting the intent to authorize additional “funding for more rock along the north bank,” in addition to “dredged material . . . to be used beneficially behind the rock.” Pls.’ Mot. for Partial Summ. J., at Ex. 43 pt.2 at 89 (Coast 2050 Report). In 1999, under the 1996 WRDA, the Corps conducted three projects along the MRGO to create 76 acres of wetlands with materials dredged from the channel. See Am. Compl. at ¶ 53. In 2004, the Corps proposed building 38 miles of rock breakwaters along the banks of the MRGO to prevent the merger of the MRGO and Lake Borgne. See Pls.’ Mot. for Partial Summ. J., Ex. 45 at 3 (U.S. Army Corps of Engineers, Louisiana Coastal Area (LCA), Louisiana, Ecosystem Restoration Study (November 2004)). The Corps noted the construction of rock breakwaters along the banks of the MRGO and southern shore of Lake Borgne “has been effectively used . . . to prevent bankline retreat and protect large areas of estuarine wetlands from further erosion and degradation.” Id. at 2. The rock breakwaters further “may also facilitate future wetland creation using dedicated dredging and/or beneficial use of dredged material . . . .” Id. Additionally, in 2004, the Corps presented in a Power Point the Breaux Act Projects, which detailed two “hydrologic restoration projects” constructed in the region and two additional “shoreline protection projects” proposed along the MRGO. Pls.’ Reply Br. Opp’n, Ex. 56 at 46–47 (U.S. Army Corps of Engineers, MRGO Studies). The proposed shoreline protections projects had an estimated cost of $45 million to benefit 495 acres of land, and the constructed hydrologic restoration projects cost $2.6 million and benefited 889 acres. Id. 33 See supra Section VI.b. - 30 - alleged taking of their land lacked the permanency required to trigger the six-year statute of limitations. Banks, 314 F.3d at 1309–10. The evidence the Court references for projects and reports on the MRGO are all publicly available documents available to plaintiffs at the time of publication. Such evidence may have, therefore, informed plaintiffs of the uncertainty as to the alleged government taking. In Banks, the government’s actions created “greater uncertainty [regarding] the Corps’ mitigation plan . . . [because] the Corps in this case actually performed its mitigation activities for several years before the filing of this action.” Banks, 314 F.3d at 1309–10. Similarly, here the numerous studies and recommendations, combined with the previously completed projects in South Lake Borgne, may demonstrate the government’s commitment to efforts to mitigate the effects of the MRGO. Although initial erosion occurred shortly after opening the MRGO, a landowner could reasonably rely on completed projects along Category Two and similar regions of the channel, as well as public reports and grants related to future projects to provide, redress for the accrued damage. A landowner who sees projects completed on their property or neighboring property and has access to comprehensive studies discussing future projects has a far different level of certainty than a landowner who observes the “Corps neither undertook nor committed itself to any mitigation.” See Mildenberger v. United States, 643 F.3d 938, 947 (Fed. Cir. 2011) (explaining “[t]here is no justifiable uncertainty due to the Corps’ promises before the 1990s because the Corps neither undertook nor committed itself to any mitigation activities”). The evidence in the record indicates plaintiffs’ claims likely stabilized at some point between 1983 and 1988. Viewing the evidence in the light most favorable to plaintiffs, however, stabilization of the plaintiffs’ takings claims related to land on the channel of Category Two occurred by 1988, when the 1988 Reconnaissance Report was published and the physical changes should have been apparent. The Court therefore concludes the evidence before it, read in the light most favorable to plaintiffs, indicates stabilization occurred no later than 1988. To toll the statute of limitations after the claims have stabilized, proposed or completed mitigation efforts by the government must create “justifiable uncertainty about the permanency of the taking,” and plaintiffs must be “aware of [mitigation] plans” during the period of time they were allegedly justifiably uncertain. Boling, 220 F.3d at 1372. Between 1988 and 2008, the Corps completed a series of projects specifically seeking to mitigate continued erosion along the banks of the MRGO. Beyond the completed projects, numerous additional studies and proposed projects suggested additional mitigation efforts would be completed along the channel. Reading the evidence of the government’s proposed and completed mitigation efforts in the light most favorable to plaintiffs, justifiable uncertainty may toll the statute of limitations on plaintiffs’ claims related to land on the channel of Category Two. See id. B. Marshlands 1. Stabilization Doctrine The Court next examines the marshland in South Lake Borgne surrounding the channel. As discussed in Category One, plaintiffs assert saltwater intrusion from the MRGO caused additional saltwater intrusion into the South Lake Borgne marshlands. See Am. Compl. at ¶ 31. - 31 - According to plaintiffs’ amended complaint, this saltwater intrusion killed the natural vegetation of the marsh, which in turn reduced the volume of root systems and caused land erosion. See Id. (“[S]altwater from the Gulf of Mexico flows up the MRGO and into the St. Bernard Parish marshes . . . . This saltwater intrusion kills the natural vegetation of the marsh and the roots of these dead plants can no longer hold the soil together along the MRGO channel banks . . . . This process has caused erosion of plaintiffs’ land.”). The MRGO was completed in 1968, and the environmental effects of the MRGO on the surrounding marshlands were readily apparent soon after.34 See Day Report at 19. A 2008 study found between the 1950s and 2000s, the South Lake Borgne region experienced dramatic hydrological changes represented by the conversion of brackish marsh to higher-salinity salt marshes, as well as an increase in the area of open water and corresponding decrease in total area of marshland.35 See id. at 44–45. In 1984, the Corps released a report which noted the marshland was disappearing at a rate of approximately 21,900 acres per year. See 1984 Initial Evaluation Study at 60–61. By 1988, the Corps released a report detailing the negative effects of saltwater intrusion and its effect on “less saline vegetation,” concluding that “[s]altwater intrusion . . . contributes significantly to marsh loss in the study area.” 1988 Reconnaissance Report at 27. Uncertainties of terrain and irregularity of the erosion resulted in plaintiffs’ reasonable inability to immediately determine the permanency of any alleged taking following completion of construction of the MRGO in 1968. Stabilization, however, does not require “the progressive environmental damage [to] stop[]” so long as the “environmental forces have substantially and permanently invaded the private property . . . .” Boling, 220 F.3d at 1371. Plaintiffs’ 15 June 2020 “list of details found in the record” references a study conducted by the Corps titled the “USACE Louisiana Coast Area, Louisiana, Land Loss and Marsh Creation, Initial Evaluation Study,” which was published in November 1984. See Pls.’ Paper at 3 (citing 1984 Initial Evaluation Study). The study in part explicitly envisions the creation of “approximately 5,000 acres” of marshland in Category Two through the beneficial use of materials dredged from the MRGO. See 1984 Initial Evaluation Study at 85. This report may indicate the government was aware of the physical ramifications of the MRGO on the marshlands of Category Two and, similarly, a reasonable landowner would have been aware of saltwater from the MRGO “permanently invad[ing] the private property” and causing erosion of the marshlands. If this is the case, plaintiffs’ claims may have stabilized as early as 1984. See Fallini, 56 F.3d at 1382 (noting “[i]t is not necessary that the damages from the alleged taking be complete and fully calculable before the cause of action accrues . . . [so long as] the ‘permanent nature’ of the taking was evident”). By at least the time the 1988 Reconnaissance Report was released, however, landowners should have both been visually aware of the physical erosion to the land and made 34 “Greater than 12,000 acres of the swamps . . . South Lake Borgne and other units were killed shortly after the opening of the MRGO . . . .” Day Report at 19. 35 “South Lake Borgne [in the 1950s] is listed as having brackish (23,773 acres) and salt (1041 [sic] acres) marsh, and swamp (668 acres). No acreage of fresh or intermediate marsh was listed for the South Lake Borgne unit. . . . The presence of cypress trees out to the edge of Lake Borgne indicate soil salinities in the fresh to intermediate range (cypress cannot tolerate salinities of more than 3-5 ppt).” Id. at 44. In the 1960s “South Lake Borgne has less intermediate (739 acres) and more brackish (19,346) marsh and 294 acres of swamp.” Id. at 45. By 2000, “South Lake Borgne had less intermediate (24 acres) and brackish (7,659) marsh and more salt marsh (9,549 acres). Swamp had been reduced to 5 acres.” Id. at 44. - 32 - aware of the changes to the land by the government’s report itself. Plaintiffs’ takings theory is based on saltwater intrusion from the MRGO leading to increased erosion of plaintiffs’ land. Am. Compl. at ¶ 31. By 1988, publicly available reports and studies made clear “[e]rosion and disintegration of the banks of the MR-GO has created many additional routes for saltwater to intrude into formerly less saline interior marshes” and therefore “salinity in the marshes has increased significantly” over the prior 20 years. 1988 Reconnaissance Report at 27. Based on the evidence currently before the Court, plaintiffs’ claims likely stabilized at some point between 1984, when the Corps issued a report noting the value of beneficial dredge materials in creating thousands of acres of marshland, and 1988, when the government published the 1988 Reconnaissance Report noting the changes in salinity and corresponding erosion in the surrounding areas. Viewing the evidence in the light most favorable to plaintiffs, however, stabilization of plaintiffs’ claims occurred by 1988 at the latest. For the purpose of the government’s motion for summary judgment, absent the justifiable uncertainty doctrine tolling the statute of limitations, the six-year statute of limitations period for plaintiffs’ claims related to the marshland of Category Two expired in 1994. See Applegate, 25 F.3d at 1583. 2. Justifiable Uncertainty For landowners to be “justifiably uncertain” as to the permanency of the alleged taking, the “question is whether the ‘predictability [and permanence] of the extent of damage to the [plaintiffs’] land’ was made justifiably uncertain by the Corps’ mitigation efforts.” Banks, 314 F.3d at 1309 (citing Applegate, 25 F.3d at 1583). A project aimed at mitigating damages would constitute justifiable uncertainty as to the permanency of the alleged taking, thus tolling the statute of limitations, if it was implemented after the date on which the Court deems plaintiffs alleged taking to have “stabilized.” Id. To determine whether proposed or actual mitigation efforts by the Corps made landowners justifiably uncertain as to the permanency of the alleged takings of land along the marshland of Category Two and therefore tolled the statute of limitations, the Court twice ordered plaintiffs to provide supplemental briefing listing proposed and completed projects affecting the justifiable uncertainty analysis of Category Two, and the government had an opportunity to respond to each. See Order, ECF No. 152; Order, ECF No. 160. All of the projects plaintiffs provided the Court as applicable to the justifiable uncertainty analysis are considered in the Court’s analysis.36 As early as 1992, the Corps began taking steps to mitigate damage to marshlands in South Lake Borgne, primarily by placing dredged material on the north bank of the MRGO so as “to develop, restore, and nourish wetlands.”37 Pls.’ Mot. for Partial Summ. J., Ex. 12 at 3 (Letter from Colonel Kenneth H. Crow to Senator John Breaux). From 1992 to 2004, the Corps detailed in various environmental assessments (“EAs”) and environmental impact statements (“EISs”) the placement of beneficial dredged materials in the marshlands in South Lake Borgne.38 36 See supra Section VII.A.2. 37 A letter from Colonel Kenneth H. Crow to Senator John Breaux detailed the Corps’ 20-year Long Term Disposal Plan for “the placement of dredged material on the north bank of the MR-GO to develop, restore and nourish wetlands.” Pls.’ Mot. for Partial Summ. J., Ex. 12 at 3 (Letter from Colonel Kenneth H. Crow to Senator John Breaux). 38 In 1992, EA #162 noted “[m]aterial removed during routine channel maintenance would be used to enhance and create approximately 555 acres of marsh and shallow open water,” which “would result in the creation and - 33 - Throughout the early 1990s, the Corps began to move forward with additional plans and projects directed to the goal of “no overall net loss of the Nation’s remaining wetlands base . . . .”39 1990 WRDA at § 307(a). In the late 1990s, and stretching into the early 2000s, the Corps continued implementing and planning various projects to further mitigate any alleged negative effects to the marshlands.40 Following Hurricane Katrina in 2005, additional projects were contemplated and implemented, which affected the marshland areas of South Lake Borgne.41 As the Federal Circuit has noted, both proposed projects and actual mitigation efforts by the government go directly to whether the landowners were “justifiably uncertain” as to the permanency of the alleged taking. Banks, 314 F.3d at 1309–10. The marshlands habitat in South Lake Borgne experienced significant fluctuations during the time period overlapping with various projects performed and proposed by the Corps.42 Between 1988 and 1997, certain areas of marshland cycled between classification as brackish marsh, intermediate marsh, and saline marsh.43 In another area of marshland in South Lake nourishment of wetlands and associated wildlife habitat.” Pls.’ Mot. for Partial Summ. J., Ex. 21 at 1 (EA #162: Marsh Enhancement/Creation – Mile 23.0 to 27.0). In 1998, EA #269 the Corps established additional disposal areas “from Miles 36.5 to 32 and Miles 49.0 to 46.5 of the MR-GO” and emphasized how the material would be placed into the disposal sites “in a manner conducive to wetland development, creating and/or restoring wetlands each cycle.” Pls.’ Mot. for Partial Summ. J., Ex. 25 at 1 (EA # 269 and EA # 269-A: South of Lake Borgne Additional Disposal Areas). In 2000, EA #269-B detailed placement of dredged material behind rock retention dikes. See Pls.’ Mot. for Partial Summ. J., Ex. 26 at 1 (EA #269-B: Additional Dispersal Areas Plus Deflection Dike and Flotation Channels). In 2001, EA #277 designated new disposal areas for beneficial use of dredged material and noted “[a]ll material would be placed into the proposed disposal sites . . . in a manner conducive to wetland development, creating and/or restoring wetlands each cycle.” Pls.’ Mot. for Partial Summ. J., Ex. 30 at 1 (EA #277: Shell Beach Disposal Areas). In 2004, EA #354 designated additional disposal areas utilized “to protect the shoreline from erosion at proposed disposal sites” through the “beneficial use of dredged material.” Pls.’ Mot. for Partial Summ. J., Ex. 33 at 1 (EA #354: Additional Disposal Area Designation Miles 66.0 to 49.0). 39 See supra Section VI.b. 40 In 1999, the Corps conducted three projects along the MRGO to create 76 acres of wetlands with materials dredged from the channel. See Am. Compl. at ¶ 53. In 2004, the Corps proposed building 38 miles of rock breakwaters along the banks of the MRGO to prevent the merger of the MRGO and Lake Borgne. See Pls.’ Mot. for Partial Summ. J., Ex. 45 at 3 (U.S. Army Corps of Engineers, Louisiana Coastal Area (LCA), Louisiana, Ecosystem Restoration Study (November 2004)). The Corps noted the construction of rock breakwaters along the banks of the MRGO and southern shore of Lake Borgne “has been effectively used . . . to prevent bankline retreat and protect large areas of estuarine wetlands from further erosion and degradation.” Id. at 2. The rock breakwaters further “may also facilitate future wetland creation using dedicated dredging and/or beneficial use of dredged material . . . .” Id. Additionally, in 2004, the Corps presented in a Power Point the Breaux Act Projects, with four projects included in the PED and two constructed projects. See Pls.’ Reply Br. Opp’n, Ex. 56 at 46–47 (U.S. Army Corps of Engineers, MRGO Studies). The PED projects included two shoreline protection projects along Lake Borgne and the MRGO, with an estimated cost of $45 million to benefit 495 acres of land, and the constructed projects included two hydrologic restoration projects in the same area, which cost $2.6 million and benefited 889 acres. Id. 41 See supra Section VI.b. 42 From the 1950s to the 2000s, in the “South Lake Borgne Unit, there was a small change in the area of intermediate marsh (24 acres) and swamp (-554 acres). There was a dramatic loss of brackish marsh (-16,115 acres) due to both construction of the MRGO canal as well as conversion of salt marsh due to higher salinity. Water area also increased (12,283) due to both MRGO canal construction and conversion of marsh to open water.” Day Report at 46. 43 “[H]abitat change was considerable between 1988 and 1997. Brackish marsh decreased from 61.5% of the property to 33% due primarily to conversion to saline marsh, which comprised 15% of the property. The increase in water habitat (32.5% of the property) appears to have resulted from both interior pond formation and from erosion along the MRGO. Intermediate marsh habitat comprised 7% of the property, most likely arising from the freshening effect of the violet siphon.” 2018 Mendelssohn Report at 4. Yet just four years later, in 2001, “saline marsh had - 34 - Borgne, brackish marsh steadily decreased, open water increased, and salt marsh experienced fluctuations until 2013, when it exponentially increased.44 Yet another area of South Lake Borgne experienced expansion of salt marshes from 1988 to 1997, but then experienced a disappearance of salt marsh in a portion of the property from 2001 to 2013.45 A landowner observing these fluctuations in salinity could reasonably attribute the hydrological changes to the implementation of various Corps projects aimed at mitigating any negative effects to the marshlands. Banks, 314 F.3d at 1309. Based on the evidence before the Court, stabilization of plaintiffs’ claims related to the marshlands of Category Two may have occurred at some point between 1984, when the Corps issued a report on the use of beneficial dredge materials in the surrounding marshland, and 1988, when the government published the 1988 Reconnaissance Report noting changes in the salinity of Category Two. Viewing the evidence in the light most favorable to plaintiffs, therefore, stabilization of the plaintiffs’ takings claims in the marshlands of Category Two occurred by 1988, when the 1988 Reconnaissance Report was published and the physical changes should have been apparent to landowners. The Court therefore concludes the evidence before it, read in the light most favorable to plaintiffs, indicates stabilization occurred no later than 1988. To toll the statute of limitations after the claims have stabilized, proposed or completed mitigation efforts by the government must create “justifiable uncertainty about the permanency of the taking,” and plaintiffs must be “aware of [mitigation] plans” during the period of time they were allegedly justifiably uncertain. Boling, 220 F.3d at 1372. The record before the Court reveals numerous examples of beneficial dredge material used by the Corps to facilitate wetlands creation in the marshlands of Category Two during the 1990s and 2000s. Reading the evidence of the government’s proposed and completed mitigation efforts in the light most favorable to plaintiffs, justifiable uncertainty may toll the statute of limitations on plaintiffs’ claims related to land on the marshlands of Category Two. See id. VIII. Analysis of Category Three – MRGO Spoil Bank Category three, the MRGO Spoil Bank corresponds to geographical “Subunit 32” of Exhibit 1 contained in the 2012 Feasibility Report. See 2012 Feasibility Report at 2-58. Subunit 32 is composed of dredged material placed along the southern shore of the MRGO, separating converted back to brackish marsh, covering 49% of the property, with little intermediate marsh (0.5%) and water comprising 39% of the property.” Id. 44 In Biloxi West, from 1968 to 2013, brackish marsh decreased from 1,926 acres to 235 acres. See 2017 Mendelssohn Report at 53. Open water increased from 296 acres in 1978 to 591 acres in 2013. Id. Salt marsh decreased from 211 acres in 1949 to zero acres in 1968–1978 but increased to 640 acres in 1988. Id. Salt marsh decreased to 578 acres in 2007 but jumped to 1,452 acres in 2013. Id. “The increase in salt marsh habitat in [Biloxi West] proceeded over time from the south as the salt marsh on the north side of the MRGO expanded in a northwest direction.” Id. at 30. 45 For the Borgnemouth property, the level of brackish marsh steadily increased up until sometime between 1978 and 1988; whereupon a sharp drop in the acreage of brackish marsh was experienced until sometime between 1997 and 2001. Again, somewhere between 2001 and 2007, however, the level of brackish marsh again dropped until the study concluded in 2013. See 2017 Mendelssohn Report at 54. The level of salt marsh also underwent significant fluctuation. Following construction of the MRGO, all salt marsh disappeared somewhere between 1978 and 1988. By 1988, however, a significant area of land (1,283 acres) became salt marsh. This level steadily dropped until ultimately reaching zero again by 2007, only to increase again by 2013 to more than 700 acres. Id. - 35 - the MRGO channel from Subunit 13 and 23.46 Subunit 32 includes the Vincent Marshlands, Livaudais, Borgnemouth, Lake Eugenie, and Biloxi properties. See JSR, ECF No. 154 at 2. A. Stabilization Doctrine As in Category Two, plaintiffs’ properties are situated on the south side of the MRGO channel banks across from South Lake Borgne. Plaintiffs present a similar theory of takings as for land along the channel in the South Lake Borgne region, arguing the dredging and operation of the MRGO caused erosion along the channel banks, widening the channel width to over 2,000 feet. Am. Compl. ¶ 30. The construction of the MRGO did not cut directly through the subunit—unlike the Central Wetlands and South Lake Borgne regions—because, until the creation of the channel, the MRGO Spoil Bank did not exist as an individual subunit. Instead, the Corps created the MRGO Spoil Bank from material dredged from the MRGO.47 Prior to dredging, “[t]he United States obtained [from plaintiffs] . . . rights of entry for construction and spoil disposal that extended 1500 feet from the channel’s original centerline,” which it used to create the MRGO Spoil Bank. Gov. Mot. for Summ. J. at 9. While the government received servitudes extending up to 1,500 feet from the centerline of the channel for construction and spoil disposal, eventually the entirety of the area granted in the servitudes was being utilized only for the channel itself. Id. at 36 (citing 1988 Reconnaissance Report at 26, 30). As noted by plaintiffs in their supplemental briefing, by at least 1983 the Corps “constructed foreshore protection test sections” along the banks of Category Three consisting of “armor coating” the shoreline with various stone and concrete configurations. See Pls.’ Supp. Paper at 29. Projects related to testing the effectiveness of various foreshore protections may indicate the government was aware of erosion of plaintiffs’ land along the banks of the channel at least by 1983. If this is the case, it may similarly be true erosion along the banks of the MRGO was such “that the permanent nature of the taking is evident and the extent of the damage is reasonably foreseeable” to landowners. Boling v. United States, 220 F.3d 1365, 1371 (Fed. Cir. 2000). The 1988 Reconnaissance Report, found the “land cut of the MRGO has increased from [a top width of] 650 feet to an average of 1,500 feet” and “the unleveed reaches are retreating at varying rates from five to over 40 feet per year.” 1988 Reconnaissance Report at 26, 30. Thus, while the government received servitudes extending up to 1,500 feet from the centerline of the channel for construction and spoil disposal, the entirety of the area granted in the servitudes was now being utilized only for the channel itself, and the average width of the channel exceeded the original channel footprint by more than 230%. Stabilization does not require “the progressive environmental damage [to] stop[]”; this nearly 1,000-foot increase in the width of the channel constitutes a substantial and permanent invasion of “private property such that the permanent nature of the taking is evident and the extent of the damage is reasonably 46 “Beneficial use” dredge material is “any use which would protect, enhance, or provide a platform for the restoration of vegetated wetlands.” Coast 2050 Report at 130. The Coast 2050 report emphasizes “[b]eneficial use of dredged material resources . . . can take on any of several forms[,]” with “[s]ediments represent[ing] one of the most important resources for building wetlands.” Id. at 129–30. Dredging activities in Louisiana “account for the removal and redeposition of 90 to 120 million cubic yards of sediment annually,” and the Coast 2050 report notes it “has been the USACE’s practice that, as long as the effort to achieve beneficial use is within the project’s base plan or federal standard cost, the USACE can and will make beneficial use of dredge material resources.” Id. 47 From 1950 to 1960, the Central Wetlands subunit received 9,191 acres of spoil material while the Jean Louis Robin received 12 acres. See Day Report at 57. - 36 - foreseeable.” Boling, 220 F.3d at 1371; see also id. at 1373 (“the takings claims accrued when the erosion has substantially encroached the parcels at issue and the damages were reasonably foreseeable.”). The uncertainties of the local terrain and difficulty in determining the location of the government’s easement meant plaintiffs’ claims did not immediately stabilize upon completion of the MRGO. Based on the evidence currently available before the Court, stabilization of plaintiffs’ claims may have occurred as early as 1983 when the government began working on foreshore protection projects intended to prevent further bank erosion. See Fallini v. United States, 56 F.3d 1378, 1382 (Fed. Cir. 1995) (noting “[i]t is not necessary that the damages from the alleged taking be complete and fully calculable before the cause of action accrues . . . [so long as] the ‘permanent nature’ of the taking was evident”). Viewing the evidence in the light most favorable to plaintiffs, however, by at least 1988 the dramatic growth of the channel and public release of the 1988 Reconnaissance Report put the landowners on adequate notice for any alleged takings claim to stabilize. Therefore, for the purposes of the cross-motions for summary judgment, absent justifiable uncertainty tolling the statute of limitations, the six-year statute of limitations period for plaintiffs’ claims for land in Category expired no later than 1994. See Applegate v. United States, 25 F.3d 1579, 1583 (Fed. Cir. 1994). B. Justifiable Uncertainty For landowners to be “justifiably uncertain” as to the permanency of the alleged taking, the “question is whether the ‘predictability [and permanence] of the extent of damage to the [plaintiffs’] land’ was made justifiably uncertain by the Corps’ mitigation efforts.” Banks v. United States. 314 F.3d 1304, 1309 (Fed. Cir. 2003) (citing Applegate, 25 F.3d at 1583). A project aimed at mitigating damages would constitute justifiable uncertainty as to the permanency of the alleged taking, thus tolling the statute of limitations, if it was implemented after the date on which the Court deems plaintiffs alleged taking to have “stabilized.” Id. at 1309. To determine whether proposed or actual mitigation efforts by the Corps made landowners justifiably uncertain as to the permanency of the alleged takings in Category Three and therefore tolled the statute of limitations, the Court twice had plaintiffs provide supplemental briefing listing proposed and completed projects affecting the justifiable uncertainty analysis of Category Three, and the government had an opportunity to respond to each. See Order, ECF No. 152; Order, ECF No. 160. All of the projects plaintiffs provided the Court as applicable to the justifiable uncertainty analysis are considered in the Court’s analysis.48 Between 1983 and 2004, the Corps completed numerous projects constructing various forms of foreshore protections and placing beneficial use dredge material along the banks of the 48 Plaintiffs’ 15 June 2020 supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category Three: The Louisiana Coastal Wetlands Restoration Plan of 1993; the Mississippi River Gulf Outlet Ecosystem Restoration Plan; and proposed and completed projects to install concrete bank protection at different points along the channel. See Pls.’ Paper at 5–6. Plaintiffs’ 30 June 2020 supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category Three: the construction of various “foreshore protection test sections” and eventually over 45 miles of foreshore protection along the MRGO spoil bank; the MRGO Back Dike Marsh Protection Project; and a proposal to provide over 30 miles of additional foreshore protection. See Pls.’ Supp. Paper at 28–30. - 37 - MRGO.49 According to the government’s own reports, the placement of dredge material in time caused the growth of new permanent vegetation and creation of new marshland habitat at the dredge material deposits.50 The regrowth of marshland from saline marshes and open waters, as confirmed by the government’s own expert report and stemming directly from the government’s depositing of beneficial use dredge material, could have left landowners in Category Three justifiably uncertain as to the permanency of the alleged taking of the surrounding land. See Boling, 220 F.3d at 1372. The government argues the work “performed to reinforce the federal levee system on the southern/western banks of the MRGO” should not “be interpreted as a promise or action to reverse or remediate the historic erosion that has taken place on any particular [p]laintiff’s property.” See Gov.’s Resp. to Pls.’ Supp. Paper at 9. As demonstrated in numerous studies and Corps’ proposals, however, the Corps used dredged material throughout the length of the channel for the benefit of the surrounding property owners. When feasible, the Corps worked with property owners to find the most beneficial use for dredged materials.51 Rather than for the sole purpose of keeping the banks of the MRGO upright, the beneficial use of dredge materials was likely recognized as being important for “a long-term goal to increase the quality and quantity of 49 EA #38, dated in 1983, detailed “[w]ork constituting of constructing six additional foreshore protection test sections along 0.45 miles of the [MRGO].” Pls.’ Mot. for Partial Summ. J., Ex. 13 at 1 (EA #38: MRGO Foreshore Protection Test Section). In 1985, EA # 47 detailed “[w]ork consist[ing] of placing 30-inch graded stone on a 9-inch shell bedding to provide foreshore protection,” with the project “located on the south bank of the [MRGO] from the Bayou Bienvenue Control structure to the end of the Chalmette Loop Hurricane Protection Levee.” Pls.’ Mot. for Partial Summ. J., Ex. 14 at 1 (EA #47: MRGO Foreshore Protection). In 1988, the Bank Reconnaissance Report detailed completed “[f]oreshore protection along 13 miles along the south bank from Bayou Bienvenue to the end of the leveed reach.” 1988 Reconnaissance Report at 14. In 1996, EA #244 detailed the completion of “protection and preservation of existing vegetated wetlands . . . on the existing south bank disposal area for the [MRGO] from approximately mile 36.0 to mile 30.0. Closure/repair of approximately 3,100 linear feet of back dike will prevent approximately 900 acres of existing fresh marsh from draining and becoming scrub-shrub habitat.” Pls.’ Mot. for Partial Summ. J., Ex. 22 at 1 (EA #244: MRGO Disposal Area Marsh Protection (Back Dike)). In 2004, EA #411 detailed a proposal for installation of articulated concrete mattress test sections along the bank of the MRGO. Pls.’ Mot. for Partial Summ. J., Ex. 36 at 1 (EA #411: Installation of Articulated Concrete Mattressing, Mile 37.4 to 36.5). 50 The government’s 2017 Mendelssohn expert report acknowledged “the deposition of MRGO dredge material on the southern flank of the MRGO converted 551 ac of salt marsh and 147 ac of water to MRGO dredge habitat . . . .” 2017 Mendelssohn Report at 17. Marsh habitat can be “created by the deposition of dredged material, which becomes vegetated over time by either marsh or terrestrial plants depending on the surface elevation of the dredged material relative to the local tidal amplitude.” Id. The Coast 2050 report provides additional evidence of the effects beneficial dredge materials can have on wetlands restoration efforts, stating the Corps and State of Louisiana “have used dredged material resources to create over 7,000 acres of subaerial land which has become vegetated wetlands.” Coast 2050 Report at 130. 51 It “has been the USACE’s practice that, as long as the effort to achieve beneficial use is within the project’s base plan or Federal standard cost, the USACE can and will make beneficial use of dredge material resources.” Id.; see also 1990 WRDA at § 307(a) (stating the Corps shall have “an interim goal of no overall net loss of the Nation’s remaining wetlands base . . . and a long-term goal to increase the quality and quantity of the Nation’s wetlands . . . .”). The Coast 2050 report emphasizes both “[t]he increased beneficial use of this dredged material resource must be an integral part of the plan to reduce Louisiana’s yearly coastal land loss” and how “the potential for the beneficial use of dredged material to address Louisiana’s coastal land loss is significant.” Id. at 129–30. The 1990 WRDA, however, does not contain any specific language related to dredge material being used to rebuilt marshland around the MRGO. See generally 1990 WRDA. - 38 - the Nation's wetlands” and therefore furthering the Corps’ goal of “no overall net loss of the Nation’s remaining wetlands base . . . .” 1990 WRDA at § 307(a).52 The use of dredged materials for the restoration of surrounding wetlands in turn likely led to landowners to be “justifiably uncertain about the permanency of the erosion and the taking . . . .” Applegate, 25 F.3d at 1583. Furthermore, Category Three is located in the same geographical area as Category Two, and those studies and proposals related to the MRGO’s erosive effects considered in the Court’s Category Two justifiable uncertainty analysis also apply here. The studies and proposals applying to both Category Two and Category Three include studies on erosion, potential restoration plans, proposed projects by the Corps to restore the MRGO to its pre-MRGO state, and legislation awarding Congressional funds for restoration efforts.53 Although some studies never resulted in final projects, others proposals and legislative acts, including multiple renewals of the WRDA, received congressional funds and led to subsequent projects, at least in part, along the MRGO. Following Hurricane Katrina in 2005, additional projects were contemplated, and Congressional funds awarded to restoration of the MRGO.54 While some of the reports and studies did not focus specifically or exclusively on the MRGO Spoil Bank, plaintiffs owning property situated along the channel, including in Category Three, could justifiably rely on proposed restorative efforts implemented at other points along the channel to conclude an alleged taking of their land lacked the permanency required to trigger the six-year statute of limitations. See Applegate, 25 F.3d at 1583. The current factual record does not clarify whether landowners were aware of the Corps’ overall restorative efforts when it pertained to their individual property 52 The language of the WRDA, combined with projects affecting Category Three proposed or completed by the Corps, may have led landowners to be justifiably uncertain as to whether the land would be repaired in pursuit of the goal of “no overall net loss of the Nation’s wetlands.” Id. There is still uncertainty in the record, however, regarding whether the specific landowners affected by the alleged taking knew of the 1990 WRDA and whether it affected how they viewed specific projects proposed or completed by the Corps affecting Category Three. See Boling, 220 F.3d at 1372. 53 See supra Section VII. 54 See supra Section VII. - 39 - in a specific subunit.55 Similar statements were made by another landowner within the subunit.56 Boling, 220 F.3d at 1372 (stating the doctrine of justifiable uncertainty depends in part on whether plaintiffs invoking the doctrine were aware of the mitigation efforts during the period they claim to be justifiably uncertain). Based on the evidence before the Court, stabilization of plaintiffs’ claims may have occurred at some point between 1983 and 1988. Viewing the evidence in the light most favorable to plaintiffs, however, stabilization of the plaintiffs’ takings claims in Category One occurred by 1988, when the 1988 Reconnaissance Report was published and the physical changes should have been apparent. The Court therefore concludes the evidence before it, read in the light most favorable to plaintiffs, indicates stabilization occurred no later than 1988. To toll the statute of limitations after the claims have stabilized, proposed or completed mitigation efforts by the government must create “justifiable uncertainty about the permanency of the taking,” and plaintiffs must be “aware of [mitigation] plans” during the period of time they were allegedly justifiably uncertain. Boling, 220 F.3d at 1372. The record highlights numerous foreshore protection projects completed along the banks of the MRGO and directly affecting erosion experienced in Category Three. Furthermore, materials dredged from the MRGO were used for the construction of wetlands in the surrounding areas, and the government issued 55 During a deposition in this case, government counsel asked the corporate representative for the Livaudais and Borgnemouth properties: Q: “[Y]ou testified that [the] MRGO had eroded into property owned by the Borgnemouth and Livaudais Companies . . . . Do you recall, at any time, the Corps of Engineers promising that it would build bank stabilization measures, or any type of revetments, that would restore the MRGO channels to the borders that you testify appear in the top portion of Exhibit 13? ... A: You’re asking me if I, personally, heard the Corps of Engineers tell us that they would restore it back to the original channel size? Q: That’s right. A: No. Q: Do you ever recall the Corps of Engineers embarking upon a project that whose purpose it was to restore the channel to its original size? A: Not to my knowledge. Q: Okay. Do you recall the Corps of Engineers ever implementing, or promising to you, or your father, or others at your company, to remediate all of the environmental damage, and erosion, that you allege is depicted in the bottom half of Exhibit 13? A: I’m not sure if I know that answer, or not. Gov.’s Reply, Ex. 2at 183:12–25, 184:1–24. 56 In the deposition of the corporate representative for Vincent properties, government counsel asked: Q: What are you aware of in terms of promises from the United States or acts by the United States that are actions you interpret to mitigate or remediate the injuries to your property at issue in this lawsuit? A: Only thing I could relate to is my experience in my being in the area fishing where you see the Corps of Engineers was working on the -- trying to install barriers on the banks of the MRGO and also . . . . That continues sporadically over the years. They would be out there doing a project, and then they would stop, and I guess it related to funding, and occasionally you read in the paper where they announced some project happening, and then you would be out there and notice it. Gov.’s Reply, Ex. 4 at 133:17–25, 134:1–9. - 40 - numerous reports and studies involving additional proposals for mitigation projects. Reading the evidence of the government’s proposed and completed mitigation efforts in the light most favorable to plaintiffs, justifiable uncertainty may toll the statute of limitations on plaintiffs’ claims related to Category Three. See id. IX. Analysis of Category Four – Biloxi Marshes Interior Biloxi Marshes Interior corresponds to geographical “Subunit 07” of Exhibit 1 contained in the 2012 Feasibility Report. See 2012 Feasibility Report at 2-58. Subunit 07 includes the Biloxi57 and Lake Eugenie properties.58 See JSR at 2. The “‘Biloxi Marshes’ is a geographical name for the remnant marshes of the St. Bernard delta, which is distinct from the Biloxi Marsh Land Corporation, a legal entity.” 2017 Mendelssohn Report at 16. The boundaries of the Biloxi Marshes Interior do not touch the MRGO channel itself, as the marshlands of South Lake Borgne separate the two. See 2012 Feasibility Report at 2-58. The Biloxi Marshes Interior subunit is located to the north of the MRGO and borders Lake Borgne’s shoreline. See id. A. Stabilization Doctrine As with the marshlands of Categories One and Two, plaintiffs’ takings theory for the Biloxi Marshes Interior is premised on gradual erosion of land due to saltwater intrusion. See Am. Compl. at ¶ 31. Documenting saltwater intrusion, a 1999 historical study details that prior to MRGO opening, the Biloxi Marshes Interior was primarily brackish and saline marsh, with a small portion classified as fresh or intermediate marsh.59 See Day Report at 54. According to 1978 measurements, the only hydrological change Biloxi Marshes Interior experienced since MRGO construction was a decrease in saline marshes.60 Id. By 1990, however, the hydrological character of marsh shifted to result in all fresh marsh disappearing, brackish marsh decreasing, and saline marsh increasing.61 Id. Further, the Biloxi Marshes Interior experienced increase in areas of open water with decrease in marshland.62 Id. The parties have not directed the Court to specific evidence suggesting a possible initial point landowners may have been aware saltwater had “substantially and permanently invaded” the marshlands of Category Four to the point where “the permanent nature of the taking is evident and the extent of the damage is reasonably foreseeable.” Boling v. United States, 220 F.3d 1365, 1371 (Fed. Cir. 2000). By the time the 1988 Reconnaissance Report was released, however, there was sufficient evidence available to plaintiffs to demonstrate substantial erosion of the marshland and make clear “environmental forces have substantially and permanently 57 “The majority of the property of the Biloxi Marsh Land Corporation . . . is located to the west of Lake Eugenie Land & Development property but still within the Biloxi marshes.” 2017 Mendelssohn Report at 23. 58 The majority of the Lake Eugenie property “is located within the area known as Biloxi Marsh.” Britsch Report at 76. 59 Prior to construction of the MRGO, the Biloxi Marsh Interior had 1,010 acres of fresh-to-intermediate marsh, 40,850 acres of brackish marsh, and 59,310 acres of salt marsh. See Day Report at 54. 60 In 1978, the subunit had 930 acres of fresh-to-intermediate marsh, 47,980 of brackish marsh, and 42,070 of saline marsh. Id. 61 By 1990, no fresh-to-intermediate marsh remained, there was 36,060 of brackish marsh, and 50,950 acres of saline marsh. Id. 62 From 1956 to 1990 open water increased from 264,410 acres to 277,380 acres. Id. - 41 - invaded the private property” necessary to trigger the stabilization doctrine. Id. at 1371; see also Fallini v. United States, 56 F.3d 1378, 1382 (Fed. Cir. 1995) (noting “[i]t is not necessary that the damages from the alleged taking be complete and fully calculable before the cause of action accrues . . . [so long as] the ‘permanent nature’ of the taking was evident”). In the report, the Corps detailed the negative effects of the MRGO on the surrounding marshlands. 1988 Reconnaissance Report at 27. These negative effects included “[s]altwater intrusion . . . [which] contributes significantly to marsh loss in the study area,” resulting in the fact “salinity in the marshes has increased significantly in the last 20 years.” Id.; see also Gov. Mot. for Summ. J. at 36–37. According to plaintiffs, saltwater intrusion resulted in erosion of their property. Am. Compl. at ¶ 31. Therefore, the rapid increase of salinity and corresponding loss of marshland noted in the 1988 Reconnaissance Report should have made landowners aware of the permanency of any taking. Boling, 220 F.3d at 1371. The evidence in the record indicates “environmental forces . . . substantially and permanently invaded” the marshlands of Category Four at some point on or before the date the 1988 Reconnaissance Report was published. Id. Viewing the evidence in the light most favorable to plaintiffs, stabilization of plaintiffs’ takings claims occurred in at least 1988, when the 1988 Reconnaissance Report both documented and reported the negative effects of saltwater intrusion on the marshland surrounding the MRGO. Therefore, for the purposes of the cross- motions for summary judgment, absent justifiable uncertainty the six-year statute of limitations period for plaintiffs’ claims in Category Four expired in 1994. See Applegate v. United States, 25 F.3d 1579, 1583 (Fed. Cir. 1994). B. Justifiable Uncertainty For landowners to be “justifiably uncertain” as to the permanency of the alleged taking, the “question is whether the ‘predictability [and permanence] of the extent of damage to the [plaintiffs’] land’ was made justifiably uncertain by the Corps’ mitigation efforts.” Banks v. United States. 314 F.3d 1304, 1309 (Fed. Cir. 2003) (citing Applegate, 25 F.3d at 1583). A project aimed at mitigating damages would constitute justifiable uncertainty as to the permanency of the alleged taking, thus tolling the statute of limitations, if it was implemented after the date on which the Court deems plaintiffs alleged taking to have “stabilized.” Id. To determine whether proposed or actual mitigation efforts by the Corps made landowners justifiably uncertain as to the permanency of the alleged takings in Category Four and therefore tolled the statute of limitations, the Court twice ordered plaintiffs to provide supplemental briefing listing proposed and completed projects affecting the justifiable uncertainty analysis of Category Four, and the government had an opportunity to respond to each. See Order, ECF No. 152; Order, ECF No. 160. All of the projects plaintiffs provided the Court as applicable to the justifiable uncertainty analysis are considered in the Court’s analysis.63 63 Plaintiffs’ 15 June 2020 supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category Four: The USACE Louisiana Coast Area Land Loss and Marsh Creation Initial Evaluation Study; the 1988 Reconnaissance Report; and the Mississippi River Gulf Outlet Ecosystem Restoration Plan’s Final Feasibility Report. See Pls.’ Paper at 6. Plaintiffs’ 30 June 2020 supplemental paper listed the following completed or proposed items applying to a justifiable uncertainty analysis for Category Four: two examples of proposed “shoreline or bank protection” and a proposed freshwater diversion. Pls.’ Supp. Paper at 27–28. - 42 - Plaintiffs do not point to any completed projects in their supplemental paper as demonstrating the Corps’ commitment to the actual implementation of mitigation projects in the Biloxi Marshes Interior. A landowner may rely, however, on “promises” by the government to complete mitigation efforts, as such promises “held out by the Corps and repeatedly renewed but never implemented, indicate[s] that ‘the landowners did not know when or if their land would be permanently destroyed.’” Banks, 314 F.3d at 1309 (quoting Applegate, 25 F.3d at 1582). Plaintiffs point to two proposed shoreline restoration projects contained in the 1993 Coastal Wetlands Planning, Protection, and Restoration Act (“CWPPRA”) and a proposed freshwater diversion detailed in the Coast 2050 report as projects proposed by the government to affect the area and supporting justifiable uncertainty on the part of landowners. See Pls.’ Supp. Paper at 27–28. The two 1993 CWPPRA project proposals involved shoreline protection along “the Lake Borgne shore of the Biloxi Marshes” and were incorporated into the 2012 Ecosystem Restoration Plan. Id. at 27. The Coast 2050 report plans for a “[w]etland sustaining diversion from the Mississippi River near Violet once the MRGO is closed.”64 Pls.’ Mot. for Partial Summ. J., Ex. 43 at 87 (Coast 2050: Toward a Sustainable Coastal Louisiana) (“Coast 2050 Report”). This freshwater diversion, similar to the Violet Siphon, was proposed to be paired with other preservation provisions related to the maintenance and repair of the Biloxi Marshland Interior marshlands.65 These project proposals occurred in a similar time as when the Corps began to move forward with other plans and projects affecting the area surrounding the MRGO and with the goal of “no overall net loss of the Nation’s remaining wetlands base . . . .”66 1990 WRDA at § 307(a). Plaintiffs argue the increased salination of the water permeating the marshes of Category Four from both the MRGO channel itself and the corresponding salinity of Lake Borgne resulted in increased erosion of the surrounding property. Am. Compl. at ¶31. Landowners could therefore be justifiably uncertain as to the permanency of such erosion-based takings when at least one of the projects proposed at some point by the government over the relevant time period was largely aimed at preserving and restoring the wetlands through diversions of fresh water and increased sediment flow. See Pls.’ Supp. Paper at 27–28. Similar to the analysis of the Violet Siphon and its effects on the justifiable certainty of landowners in Category One, a recommendation by the government to implement a freshwater siphon to create sediment flow and combat erosion constitutes justifiable uncertainty as to the permanency of the taking.67 64 The proposal states: “Wetland sustaining diversion from the Mississippi River near Violet once the MRGO is closed. A 2,000 to 5,000 cfs diversion from the Mississippi River through the Violet Canal to sustain the Central Wetlands and Biloxi Marshes would be built. Such a diversion could not be effective until the MRGO is closed. This strategy is estimated to preserve moderate amounts of the marshes in the Central Wetlands adjacent to Lake Borgne.” Coast 2050 Report at 87 (emphasis in original). 65 Some of the provisions include: (1) “Dedicated delivery of sediment for marsh building”; (2) “Maintain shoreline integrity of Lake Borgne and protect shoreline of Biloxi Marshes”; and (3) “Construct breaches between MRGO and Lake Borgne . . . to contain the created marsh.” Id. at 87–89. 66 See supra Section VI.b. 67 Mr. Charles Ogden, the general counsel of Lake Eugenie and Biloxi, described in his deposition the landowner’s uncertainty regarding the proposed siphon project: “So we still had hope that we could get some freshwater diversion at least, or do something. Then when they came out with the 2009 Draft EIS for MRGO for the first time then we realized that they had what they called a TSP, the tentatively selected plan, that, for the first time, showed us - 43 - Although the project proposal for the siphon states it will not be “effective” unless the MRGO is closed, plaintiffs are further able to point to other proposed or completed projects corresponding with the Corps’ goal of “no overall wetland loss” and, in some instances, specifically aimed at preventing the merging of the MRGO and Lake Borgne.68 While the MRGO did not cut directly through the Biloxi Marshes Interior, a landowner could be made justifiably uncertain as to the permanency of a taking in part based on projects planned or completed by the government along the MRGO to prevent salt water from further permeating the channel banks, such as projects related to shoreline stabilization seeking to prevent the merging of Lake Borgne and the MRGO. See Banks, 314 F.3d at 1309 (noting a landowner need not receive “a legal binding promise or duty or a matter requiring congressional appropriation” to be justifiably uncertain, because the “mere promise” of mitigation efforts, “held out by the Corps and repeatedly renewed but never implemented, indicate[s] that the landowners did not know when or if their land would be permanently destroyed”) (quotation marks and citations omitted). Here, plaintiffs cite no completed projects in their supplemental paper, but the studies, recommendations, and eventual closing of the MRGO demonstrate the government’s commitment to mitigation efforts. The projects proposed in various government reports include a “[w]etland sustaining [freshwater] diversion,” “[d]edicated delivery of sediment for marsh building,” “[m]aintaining shoreline integrity of Lake Borgne and protect shoreline of Biloxi Marshes,” and “[c]onstricting breaches between MRGO and Lake Borgne with created marshes.” Coast 2050 Report at 87–89. In 2006, Congress mandated the Corps develop a comprehensive plan to de-authorize the MRGO69 and in 2009 officially closed the MRGO. See Pls.’ Mot. for Partial Summ. J., Ex. 51 at 1 (Mississippi River-Gulf Outlet Deep Draft De-authorization Study); 2012 Feasibility Report at S-2. At the point Congress mandated a plan to de-authorize the MRGO, landowners could be justifiably uncertain as to the effects of the freshwater diversion on the permanency of any salinity-based takings. As confirmed during a landowner’s deposition, it was not until 2012, the year of the final feasibility report, landowners in the Biloxi Marshes Interior were not included in any future restoration plan.70 that the restoration plans for the damage done by MRGO was going to be practically everything on the NW side of the dam and very little, if any, on the bottom side.” Gov.’s Reply, Ex. 3 at 133:18–25, 134:1–5. 68 In the 2004 USCAE LCA Ecosystem Restoration study, the Corps warned that the “rate of wetland loss in the area is accelerating” and “[r]apid action is required to protect the integrity of the southern Lake Borgne shoreline and to prevent continued erosion of the MRGO channel banks from ocean going vessel wakes.” Pls.’ Mot. for Partial Summ. J., Ex. 45 at 31 (U.S. Army Corps of Engineers, Louisiana Coastal Area (LCA), Louisiana, Ecosystem Restoration Study (November 2004)). The Corps proposed building 38 miles of rock breakwaters along the banks of the MRGO to prevent the merger of the MRGO and Lake Borgne, noting such construction “has been effectively used . . . to prevent bankline retreat and protect large areas of estuarine wetlands from further erosion and degradation.” Id. at 2. The rock breakwaters further “may also facilitate future wetland creation using dedicated dredging and/or beneficial use of dredged material . . . .” Id. Additionally, in 2004, the Corps presented in a Power Point the Breaux Act Projects, with four projects included in the PED and two constructed projects. Pls.’ Reply Br. Opp’n, Ex. 56 at 46–47 (U.S. Army Corps of Engineers, MRGO Studies). The PED projects included two shoreline protection projects along Lake Borgne and the MRGO with an estimated cost of $45 million to benefit 495 acres of land, and the constructed projects included two hydrologic restoration projects in the same area which cost $2.6 million and benefited 889 acres. Id. 69 See supra Section VI.b. 70 Mr. Ogden states: “So we realized that all the erosion that was still there caused by MRGO to the properties there, and there is some interworkings in some marsh fill in this area on Lake Borgne but none in the further up marshes. We realied [sic] then that there is no further plan for restoration. This is the final — Which in 2010 there - 44 - Viewing the evidence in the light most favorable to plaintiffs, stabilization of the plaintiffs’ takings claims in Category Four occurred by at least 1988, when the 1988 Reconnaissance Report was published and the physical changes should have been apparent. The Court therefore concludes the evidence before it, read in the light most favorable to the plaintiff, indicates stabilization occurred no later than 1988. To toll the statute of limitations after the claims have stabilized, proposed or completed mitigation efforts by the government must create “justifiable uncertainty about the permanency of the taking,” and plaintiffs must be “aware of [mitigation] plans” during the period of time they were allegedly justifiably uncertain. Boling, 220 F.3d at 1372. The proposed freshwater diversion, although never completed, could leave landowners in Category Four justifiably uncertain as to the permanency of takings allegedly stemming from salinity-based erosion. Further, plaintiffs highlight shoreline protection and wetlands creation projects proposed in the 1990s and 2000s as contributing to justifiable uncertainty. Reading the evidence of the government’s proposed and completed mitigation efforts in the light most favorable to the plaintiff, justifiable uncertainty may toll the statute of limitations on plaintiffs’ claims related to Category Four. See id. X. Analysis of Category Five – Biloxi Marshes Exterior Category Five, the Biloxi Marshes Exterior, corresponds to geographical “Subunit 06” of Exhibit 1 contained in the 2012 Feasibility Report. See 2012 Feasibility Report at 2-58. Subunit 06 includes the Biloxi71 and Lake Eugenie properties.72 See JSR at 2. The “‘Biloxi Marshes’ is a geographical name for the remnant marshes of the St. Bernard delta, which is distinct from the Biloxi Marsh Land Corporation, a legal entity.” 2017 Mendelssohn Report at 16. The Biloxi Marshes Exterior does not touch the MRGO channel itself, but rather is separated from the channel by subunit 18. See 2012 Feasibility Report at 2-58. Biloxi Marshes Exterior is bordered by Chandeleur Sound on the east and is bordered by the Mississippi Sound miles to its north. See id. The most northeastern portion of the property “is an isolated island chain” “characterized by scattered islands, bays and large open water lakes.” Gov. Mot. for Summ. J., Ex. 12 at 23 (The Biloxi Marsh Stabilization and Restoration Plan) (“King Report”). A. Stabilization Doctrine Plaintiffs’ takings theory for the Biloxi Marshes Exterior and other property not directly bordering the MRGO is based on erosion caused by saltwater intruding onto the property from the MRGO, rather than direct erosion occurring on the banks of the MRGO itself. See Am. Compl. at ¶31. The government argues the MRGO did not have an erosive effect on the Biloxi Marshes Exterior, but instead, “[t]he proximity of Plaintiffs’ properties to the marine influences of Breton Sound, rising sea levels, subsidence, open exposure to wind waves and storm surge, and alterations to hydrology by human development caused salinity increases, habitat changes, was a report and then in 2012 confirmed we’re being left out of the restoration, at least in the areas, you know, south and east of the dam in the areas in the Biloxi Marsh and Lake Eugenie to the east.” Gov.’s Reply, Ex. 3 at 134:6–18. 71 “The majority of the property of the Biloxi Marsh Land Corporation . . . is located to the west of Lake Eugenie Land & Development property but still within the Biloxi marshes.” 2017 Mendelssohn Report at 23. 72 The majority of the Lake Eugenie property “is located within the area known as Biloxi Marsh.” Britsch Report at 76. - 45 - erosion and land loss on Plaintiffs’ properties throughout the Twentieth Century” and “will continue to cause salinity increases, habitat changes, erosion and land loss on Plaintiffs’ properties now and in the future.” Gov. Mot. for Summ. J. at 25. Prior to construction of the MRGO, the majority of the Biloxi Marshes Exterior was located in a salt marsh habitat.73 Following completion of the MRGO in 1968, the Biloxi Marshes Exterior experienced an increase in the area of brackish marsh—so less salty—instead of the increase in salt marsh observed in Categories One and Two.74 The frequency of salt marshland has oscillated throughout subsequent years.75 Additionally, as compared to other subunits, the Biloxi Marshes Exterior opens directly to various sounds, and the entire area “is under constant threat from active erosional forces generated as wave fetch developments across the exposed bays and lakes. This problem occurs on a daily basis and is exacerbated during tropical events.” King Report at 27. The parties have not directed the Court to any specific evidence suggesting a possible first point landowners may have been aware the saltwater had “substantially and permanently invaded” Category Five to the point where “the permanent nature of the taking is evident and the extent of the damage is reasonably foreseeable.” Boling v. United States, 220 F.3d 1365, 1370 (Fed. Cir. 2000). Although the area did not experience substantial changes in hydrological conditions upon the completion of the MRGO compared to other subunits, by the time the 1988 Reconnaissance Report was published there was sufficient evidence available to plaintiffs to show substantial encroachments of saltwater into the marshlands was generally occurring throughout the delta. See 1988 Reconnaissance Report at 27; see also Fallini v. United States, 56 F.3d 1378, 1382 (Fed. Cir. 1995) (noting “[i]t is not necessary that the damages from the alleged taking be complete and fully calculable before the cause of action accrues . . . [so long as] the ‘permanent nature’ of the taking was evident”). The 1988 Reconnaissance Report explicitly highlights how both “[s]altwater intrusion . . . contributes significantly to marsh loss in the study area” and “salinity in the marshes has increased significantly in the last 20 years. 1988 Reconnaissance Report at 27. The report further notes this higher salinity has “reduced the amount” of certain plant life, with “less saline vegetation . . . greatly reduced by saltwater intrusion.” Id. By 1988 at the latest, the government’s reports and the physical changes to the area made clear “environmental forces had substantially and permanently invaded the private property such that the permanent nature of the taking is evident and the extent of the damage is reasonably foreseeable,” thus beginning the six-year statute of limitations for property owners in the Biloxi Marshes Exterior. Boling, 220 F.3d at 1371. Therefore, viewing the evidence in the light most favorable to the plaintiff for the purposes of the cross-motions for summary judgment, absent 73 “Prior to MRGO construction, 99% of [Lake Eugenie East] property was located in salt marsh habitats along the outer fringes of the remnant of St. Bernard Delta.” 2017 Mendelssohn Report at 16. The property “consisted of salt marsh (29,906 ac), brackish marsh (787 ac), and water (43,021 ac) habitats in 1949.” Id (citations omitted). 74 “As of 1978, [Lake Eugenie East] was still primarily salt marsh (23,576 ac), although an area of brackish marsh (3,478 ac) was present in the northwestern portion . . . that had mostly converted from salt marsh in 1968.” Id. at 18. 75 In 1988, the habitat of the Biloxi Marshes Exterior “was still primarily salt marsh habitat (58%, 24,949).” Id. In 2001, the property “was still primarily salt marsh (22,663 ac).” Id. at 20. - 46 - justifiable uncertainty the six-year statute of limitations period for plaintiffs’ claims in Category Five expired in 1994. See Applegate v. United States, 25 F.3d 1579, 1583 (Fed. Cir. 1994). B. Justifiable Uncertainty For landowners to be “justifiably uncertain” as to the permanency of the alleged taking, the “question is whether the ‘predictability [and permanence] of the extent of damage to the [plaintiffs’] land’ was made justifiably uncertain by the Corps’ mitigation efforts.” Banks v. United States. 314 F.3d 1304, 1309 (Fed. Cir. 2003) (citing Applegate, 25 F.3d at 1583). A project aimed at mitigating damages would constitute justifiable uncertainty as to the permanency of the alleged taking, thus tolling the statute of limitations, if it was implemented after the date on which the Court deems plaintiffs alleged taking to have “stabilized.” Id. To determine whether proposed or actual mitigation efforts by the Corps made landowners justifiably uncertain as to the permanency of the alleged takings in Category Five, and toll the statute of limitations, the Court twice requested plaintiffs provide supplemental briefing listing proposed and completed projects affecting the justifiable uncertainty analysis. See Order, ECF No. 152; Order, ECF No. 160. The projects plaintiffs provided the Court as applicable are considered in the Court’s analysis.76 For the justifiable uncertainty analysis, plaintiffs do not cite any completed projects and reference only one proposed project directed at potentially mitigating damage to the marshlands of Category Five: The Bonnet Carre Freshwater Diversion. See Pls.’ Paper at 6; Pls.’ Supp. Paper at 24–26. A freshwater diversion at Bonnet Carre was first proposed in 1984 and was authorized by Congress pursuant to the Water Resources Development Act of 1988.77 See 2012 Feasibility Report at 2-87; Pls.’ Supp. Paper at 24–25. The diversion would have “provided for 76 Plaintiffs’ 15 June 2020 supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category Five: The USACE Louisiana Coast Area Land Loss and Marsh Creation Initial Evaluation Study; the 1988 Reconnaissance Report; and the Mississippi River Gulf Outlet Ecosystem Restoration Plan’s Final Feasibility Report. See Pls.’ Paper at 6. None of the sources cited in plaintiffs’ 15 June supplemental paper include proposed or completed projects directly affecting Category Five. Id. The fact these projects do not provide any examples of instances where the Corps directly “undertook [or] committed itself to any mitigation activities” means landowners could not rely on these projects to be justifiably uncertain as to the permanency of a taking. Mildenberger, 643 F.3d at 947. At oral argument, plaintiffs referenced the proposed Bonnet Carre spillway as the only project which was directly related to Category Five. See ECF No. 159 at 3:20:56–3:24:04 (recording of oral argument). Plaintiffs’ 30 June 2020 supplemental paper noted only the proposed Bonnet Carre Freshwater Diversion project as relevant to a justifiable uncertainty analysis of Category Five. See Pls.’ Supp. Paper at 24–26. 77 The 1988 WRDA provided funds for “the project for environmental enhancement, Mississippi and Louisiana Estuarine Areas, Mississippi and Louisiana: Report of the Chief Engineers, dated May 19, 1986 . . . .” See Water Resource Development Act of 1988, Pub. L. No. 100-676, tit. I § 3(a)(8), 102 Stat. 4012 (1988). This project, initially proposed in a 1984 Corps study, called for the creation of a freshwater diversion program through “breaching the natural riverbank” at different locations, some of which included property owned by the State of Louisiana. 1984 Initial Evaluation Study at 82. Further, as noted by the government, Category Five does not border Lake Borgne and “[p]laintiffs acknowledge[] this federal proposal was never built and was killed in 1996 when the State of Louisiana expressed its opposition.” Gov’t’s Resp. to Pls.’ Supp. Paper at 7. There is no discussion or detail in the record as to why Bonnet Carre project, funded by the 1988 WRDA, was not pursued after the State of Louisiana expressed its opposition. Plaintiff, however, does not dispute the project was never built and the Corps did not work on the project at least after the state expressed its opposition. See Pls.’ Supp. Paper; ECF No. 159 at 3:23:10–3:24:00 (recording of oral argument). - 47 - the diversion of Mississippi River water to Lake Pontchartrain, through the existing Bonnet Care Spillway . . . to reduce saltwater intrusion affecting Lakes Maurepas, Pontchartrain, and Borgne and the Mississippi Sound and adjacent wetlands.” Pls.’ Supp. Paper at 25. The Bonnet Carre freshwater diversion project was never constructed, as the State of Louisiana expressed opposition to a large diversion of freshwater into Lake Pontcharain and declined to participate in the project. See id. at 26 (“The State of Louisiana subsequently expressed opposition to a large diversion of freshwater into Lake Pontchartrain due to water quality concerns, and in July 1996 declined to participate further in the project.”). Following the 1996 rejection by the State of Louisiana, the only other proposal related to the Bonnet Carre spillway plaintiffs provide in the 31 July 2020 supplemental paper’s timeline of the proposed project is a 2012 MRGO Ecosystem restoration report. See id. (citing 2012 Feasibility Report at 2-87). This report itself only states the proposed Bonnet Carre freshwater diversion project “could be considered” as a possible project to fulfill the 2012 report’s “call[] for considering the diversion of freshwater from the Mississippi River for restoring the Lake Borgne ecosystem.” Id. (citing 2012 Feasibility Report at 2-87). Plaintiffs acknowledge the State of Louisiana declined to participate in the project in 1996, and the Bonnet Carre freshwater diversion project was never completed. See id. Plaintiffs argue, however, the Bonnet Carre freshwater diversion is “still an authorized project” under the 1988 WRDA and point to a 2012 ecosystem restoration plan calling for the “considering [of] the diversion of fresh water from the Mississippi River” at the Bonnet Carre diversion location as evidence the proposed project continues to create justifiable uncertainty. Id. Even assuming the proposed freshwater diversion resulted in justifiable uncertainty until Louisiana expressed its opposition to the project in 1996, there is at least an eleven-year gap in plaintiffs’ timeline of the proposed, but explicitly rejected, project. See id. at 25–26. It is not enough the project remained “authorized” by the 1988 WRDA, in the face of the state’s opposition and no evidence in the record of plans to complete the project after 1996, for landowners in Category Five to have remained justifiably uncertain as to the permanency of the alleged taking during at least this 11-year period. Banks, 314 F.3d at 1309. Viewing the evidence in the light most favorable to plaintiffs, stabilization of the plaintiffs’ takings claims in Category Five may have occurred as late as 1988, when the 1988 Reconnaissance Report published and physical changes should have been apparent. To toll the statute of limitations after the claims stabilized, proposed or completed mitigation efforts by the government must create “justifiable uncertainty about the permanency of the taking,” and plaintiffs must be “aware of [mitigation] plans” during the period of time. Boling, 220 F.3d at 1372. Given the proposed spillway discussion, viewing the summary judgment evidence in the light most favorable to plaintiffs, the Bonnet Carre diversion may have been sufficient to create justifiable uncertainty as to the permanency of the alleged taking and toll the statute of limitations until as late as 1996, but then all project discussion ceased. In the absence of any further discussion, or other project creating justifiable uncertainty after 1996, the statute of limitations would no longer be tolled. See Mildenberger v. United States, 643 F.3d 938, 947 (Fed. Cir. 2011) (“There is no justifiable uncertainty due to the Corps’ promises before the 1990s because the Corps neither undertook nor committed itself to any mitigation activities.”). Accordingly, landowners had until 2002 to file suit. Id. - 48 - The Court granted the parties multiple opportunities to provide detail regarding projects affecting various portions of property at issue. See, e.g., Order, ECF No. 156; Order, ECF No. 160. Plaintiffs cited no other projects, either proposed or completed, which would continue to toll the statute of limitations beyond 2002. After careful review of the voluminous record, the Court is further unable to locate any other projects which would cause a landowner in Category Five to remain justifiably uncertain. Based on the record presented by the parties, landowners in Category Five could have only been justifiably uncertain until as late as 1996, and plaintiffs’ statute of limitations could have been tolled only until as late as 2002. Banks, 314 F.3d at 1309. XI. Analysis of Category Six – Eloi Bay Eloi Bay corresponds to geographical “Subunit 18” of Exhibit 1 contained in the 2012 Feasibility Report. See 2012 Feasibility Report at 2-58. Subunit 18 includes Terre Aux Boeufs,78 Lake Eugenie,79 and Biloxi properties.80 See JSR at 2. Eloi Bay is situated on the northern MRGO channel banks east of South Lake Borgne subunit and extends north into the marshlands below the Biloxi Marshes Interior and Exterior. See 2012 Feasibility Report at 2-58. Eloi Bay extends the length of the channel into Chandeleur Sound. Id. There are thus two distinct types of land within Category Six: property situated on the banks of the channel and the remaining marshlands. A. Channel 1. Stabilization Doctrine As with Category Two, plaintiffs’ properties are situated along the northern shore of the MRGO channel banks, and plaintiffs argue the dredging and operation of the MRGO caused erosion to widen the width of the channel banks to over 2,000 feet. Am. Compl. ¶ 30. The MRGO cut directly through Eloi Bay and opened a portion of the property to saltwater. The subunit was also previously open to Breton Sound and subject to natural erosive processes and saltwater intrusion.81 See King Report at 31. Prior to dredging, “[t]he United States obtained [from plaintiffs] . . . rights of entry for construction and spoil disposal that extended 1500 feet from the channel’s original centerline.” Gov. Mot. for Summ. J. at 9. Thus, while the government received servitudes extending up to 1,500 feet from the centerline of the channel for construction and spoil disposal, by 1988 erosion of the channel banks meant the entirety of the area granted in the servitudes was utilized only for the channel itself. Id. at 36 (citing 1988 Reconnaissance Report at 26, 30). 78 The Terra Aux Boeufs property “consists of two sections, Terre aux Boeufs-East, located north of the MRGO, and Terre aux Boeufs-West, located south of the MRGO.” 2018 Mendelssohn Report at 35. The Eastern portion of the property is in Eloi Bay. See 2012 Feasibility Report at 2-58. 79 For Lake Eugenie, a portion of the Eastern property is in Eloi Bay. Id. 80 Biloxi owns two separate property groups, Biloxi East and Biloxi West. “The majority of the [Biloxi East] property . . . is located to the west of Lake Eugenie Land & Development property, but still within the Biloxi marshes.” 2017 Mendelssohn Report at 23. 81 “The majority of this [Eloi Bay] is under constant threat from marginal erosion forces generated as wave fetch develops across Breton Sound and rolls into the interior exposed lakes. This problem occurs on a daily basis and is exacerbated during tropical events. This region is the southernmost area of interest of this marsh stabilization and restoration plan.” King Report at 31. - 49 - Plaintiffs’ 31 July 2020 “list of citations and excerpts” details how, by at least 1985, the Corps was “conduct[ing] a number of projects, including installation of foreshore protection . . . .” See Pls.’ Supp. Paper at 31. The installation of foreshore protection along the MRGO at least as early as 1985 may have been in response to the government’s recognition of significant and continued erosion occurring along the channel of the MRGO. The government’s possible awareness of physical changes occurring along the MRGO sufficient to stabilize plaintiffs’ claims may in turn indicate landowners were aware of all of the facts necessary to stabilize their takings claims. See Boling v. United States, 220 F.3d 1365, 1372 (Fed. Cir. 2000). In 1988, the Corps publicly published the 1988 Reconnaissance Report, which documents erosion along the banks of the MRGO, noting the “land cut of the MRGO has increased from [a top width of] 650 feet to an average of 1,500 feet” and “the unleveed reaches are retreating at varying rates from five to over 40 feet per year.” 1988 Reconnaissance Report at 26, 30. Stabilization does not require “the progressive environmental damage [to] stop[]”; this nearly 1,000-foot increase in the channel width, and continued erosion along the banks, would provide sufficient physical evidence to landowners a substantial and permanent invasion of “private property such that the permanent nature of the taking is evident and the extent of the damage is reasonably foreseeable.” Boling, 220 F.3d at 1371. The evidence available in the record related to MRGO channel widening through bank erosion indicates there was a “substantial and permanent” invasion of private property sufficient to trigger the doctrine of stabilization at some point between at least 1985, when the evidence in the record indicates the government was conducting foreshore protection projects along the MRGO channel, and 1988, the year the 1988 Reconnaissance Report detailed the substantial and continued widening of the MRGO channel. For the purpose of the government’s motion for summary judgment, by at least 1988 the dramatic growth of the channel and publication of the 1988 Reconnaissance Report put the landowners on adequate notice for a taking to accrue. Therefore, absent justifiable uncertainty tolling the statute of limitations, the six-year statute of limitations period for plaintiffs’ claims along the channel of Category Two expired in 1994. See Applegate v. United States, 25 F.3d 1579, 1583 (Fed. Cir. 1994). 2. Justifiable Uncertainty For landowners to be “justifiably uncertain” as to the permanency of the alleged taking, the “question is whether the ‘predictability [and permanence] of the extent of damage to the [plaintiffs’] land’ was made justifiably uncertain by the Corps’ mitigation efforts.” Banks v. United States. 314 F.3d 1304, 1309 (Fed. Cir. 2003) (citing Applegate, 25 F.3d at 1583). A project aimed at mitigating damages would constitute justifiable uncertainty as to the permanency of the alleged taking, thus tolling the statute of limitations, if it was implemented after the date on which the Court deems plaintiffs alleged taking to have “stabilized.” Id. To determine whether proposed or actual mitigation efforts by the Corps made landowners justifiably uncertain regarding permanency of alleged takings in Category Six, and along the MRGO channel, and therefore tolled the statute of limitations, the Court twice ordered plaintiffs to provide supplemental briefing listing proposed and completed projects. See Order, ECF No. - 50 - 152; Order, ECF No. 160. All of the projects plaintiffs provided the Court as applicable to the justifiable uncertainty analysis are considered in the Court’s analysis.82 Category Six is located in the same geographical area as Category Two; similar projects, studies, and proposed projects, applying to Category Two’s justifiable uncertainty analysis apply here—including studies on erosion, potential restoration plans, and proposed projects by the Corps to restore Category Six to its pre-MRGO state.83 Although some studies never received approval, others, including multiple renewals of the WRDA, received congressional funds and led to subsequent projects, at least in part, along the MRGO. See supra Section VII. Following Hurricane Katrina in 2005, additional projects were contemplated, and Congressional funds awarded to restoration of the MRGO.84 A landowner need not receive “a legal binding promise or duty or a matter requiring a congressional appropriation” to be justifiably uncertain as to the permanency of an alleged taking. Banks, 314 F.3d at 1309. Rather, the “mere promise” of mitigation efforts, “held out by the Corps and repeatedly renewed but never implemented, indicate[s] that ‘the landowners did not know when or if their land would be permanently destroyed.’” Id. (quoting Applegate, 25 F.3d at 1583). Based on the results of various EISs and EAs, the Corps began a series of projects along the channel to address the environmental and physical impact of the MRGO. From 1998 to 2002, the Corps completed projects directed towards building retention dikes and the use of beneficial dredged material from the MRGO.85 While some of the studies and proposed projects referenced by plaintiffs did not focus specifically or exclusively on Eloi Bay, plaintiffs owning property situated on the channel itself could justifiably rely on proposed restorative efforts implemented at other points along the channel to conclude an alleged taking of their land lacked the permanency required to trigger the six-year statute of limitations. Applegate, 25 F.3d at 1583. 82 Plaintiffs’ 15 June 2020 supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category Six: The USACE Louisiana Coast Area Land Loss and Marsh Creation Initial Evaluation Study; the 1988 Reconnaissance Report; the Mississippi River Gulf Outlet Ecosystem Restoration Plan’s Final Feasibility Report; proposed and completed beneficial uses of dredged materials; and proposed and completed projects related to the construction of retention dikes and bank stabilization structures along the channel. See Pls.’ Paper at 6–7. Plaintiffs’ 30 June 2020 supplemental paper listed the following completed or proposed items as relevant to a justifiable uncertainty analysis for Category Six: installation of foreshore protection; beneficial use of dredged materials; proposed freshwater diversions into the marshland. See Pls.’ Supp. Paper at 31. 83 See supra Section VII. 84 See supra Section VII. 85 In 1998, EA #269 and #269-A detailed plans to construct additional disposal areas “from Miles 36.5 to 32 and Miles 49.0 to 46.5 of the MR-GO” and emphasized how the material would be placed into the disposal sites “in a manner conducive to wetland development, creating and/or restoring wetlands each cycle.” Pls.’ Mot. for Partial Summ. J., Ex. 25 at 1 (EA # 269 and EA # 269-A: South of Lake Borgne Additional Disposal Areas). In 2000, EA #269-B detailed placement of dredged material behind rock retention dikes. See Pls.’ Mot. for Partial Summ. J., Ex. 26 at 1 (EA #269-B: Additional Dispersal Areas Plus Deflection Dike and Flotation Channels). Lastly, in 2002, EA #349 proposed to “designate additional disposal areas [and] construct closure and bank stabilization structures . . . between Mile 32 and Mile 27” of the MRGO. Pls.’ Mot. for Partial Summ. J., Ex. 32 at 1 (EA #349: MRGO Miles 32-27 Additional Disposal Areas- Hopedale Marshes). EA #349 further made clear [d]redged material removed from the MR-GO channel project during routine maintenance events would be utilized beneficially for the creation of wetlands in shallow, open-water areas adjacent to the MR-GO.” Id. - 51 - The evidence which the Court references for government projects and reports related to the MRGO are all public documents available to plaintiffs at the time of their publication. Such evidence was therefore available to plaintiffs to inform them of the uncertainty as to the alleged government taking. “[P]roposals to correct the damage” done to the land put forward by the government can “further complicate[] ascertaining the extent and nature of the consequences” of the physical taking enough to trigger the doctrine of justifiable uncertainty. Applegate, 25 F.3d at 1584. Although initial erosion occurred shortly after opening the MRGO, a landowner could reasonably rely on completed projects along similar regions of the channel and public reports and grants related to future projects to provide redress for the accrued damage. See Banks, 314 F.3d at 1309 (noting a landowner need not receive “a legal binding promise or duty or a matter requiring congressional appropriation” to be justifiably uncertain, because the “mere promise” of mitigation efforts, “held out by the Corps and repeatedly renewed but never implemented, indicate[s] that the landowners did not know when or if their land would be permanently destroyed”) (quotation marks and citations omitted). A landowner who sees projects completed on their property or neighboring property and has access to comprehensive studies discussing future projects is much more likely to be justifiably uncertain than a landowner who believes the “Corps neither undertook nor committed itself to any mitigation.” See Mildenberger v. United States, 643 F.3d 938, 947 (Fed. Cir. 2011). Plaintiffs’ takings claims with regard to the land located along the MRGO channel in Category Six stabilized at some point between 1985 and 1988. Viewing the evidence in the light most favorable to plaintiffs, however, stabilization of plaintiffs’ takings claims in Category One occurred by 1988, when the 1988 Reconnaissance Report was published and the physical changes should have been apparent. The Court therefore concludes the evidence before it, read in the light most favorable to plaintiffs, indicates stabilization occurred no later than 1988. To toll the statute of limitations after the claims have stabilized, proposed or completed mitigation efforts by the government must create “justifiable uncertainty about the permanency of the taking,” and plaintiffs must be “aware of [mitigation] plans” during the period of time they were allegedly justifiably uncertain. Boling, 220 F.3d at 1372. The record contains various examples of proposed and completed foreshore protection and beneficial use of dredge material projects along the channel of the MRGO affecting the land along the channel in both Category Six and other categories of land. Reading the evidence of the government’s proposed and completed mitigation efforts in the light most favorable to plaintiffs, justifiable uncertainty may toll the statute of limitations on plaintiffs’ claims related to land on the channel of Category Six. See id. B. Marshland 1. Stabilization Doctrine As discussed in Category One, plaintiffs assert saltwater intrusion from the MRGO killed the natural vegetation of the marsh, which in turn reduced the volume of root systems and caused erosion of plaintiffs’ land. Am. Compl. at ¶ 31. Prior to construction of the MRGO, Eloi Bay was located in salt and brackish marsh habitat.86 Upon construction and operation of the MRGO, 86 In 1958, Eloi Bay was “mainly brackish (18,039 acres) and salt (17,467) marsh.” See Day Report at 44. In 1960, “there was a loss of brackish marsh (-10,872) and an increase in salt marsh (832 acres). These changes were due to an increase in open water (4,960) acres.” Id. at 47. - 52 - the total area of salt marsh subsequently increased and the total area of brackish marsh decreased.87 As with Category Five, Eloi Bay opens directly to Chandeleur Sound and “is under constant threat from marginal erosion forces generated as wave fetch develops across Breton Sound and rolls into the interior exposed lakes. This problem occurs on a daily basis and is exacerbated during tropical events. This region is the southernmost area of interest of this marsh stabilization and restoration plan.” King Report at 31. Category Six, although subject to similar erosive processes from Chandeleur Sound as Category Five, experienced a notable increase in saline marsh and a decrease in brackish marsh following the opening of the MRGO. Day Report at 57. While the Court has already noted the uncertainty in the terrain and irregularity of erosion of Category Six regarding land around the channel, such uncertainties are even more pronounced when proceeding into the marshlands. Stabilization, however, does not require the progressive environmental damage to stop so long as the landowners were or should be aware “environmental forces have substantially and permanently invaded the private property . . . .” Boling, 220 F.3d at 1371. Plaintiffs’ 15 June 2020 “list of details found in the record” references as related to projects affecting Category Six a study conducted by the Corps titled the “USACE Louisiana Coast Area, Louisiana, Land Loss and Marsh Creation, Initial Evaluation Study” published in November 1984. See Pls.’ Paper at 7 (citing 1984 Initial Evaluation Study). The 1984 Corps’ study specifically envisioned the “creat[ion of] 5,000 acres of marsh with material obtained from the maintenance dredging of the Mississippi River-Gulf Outlet,” which would be “placed to an elevation for creating marsh.” 1984 Initial Evaluation Study at 85. As with Category Two, the report’s specific plans to create “approximately 5,000 acres” of marshland in a region encompassing the marshlands of Category Six through the use of beneficial dredge materials may indicate the government was aware of the need for specific “marsh creation” to counteract the effect of erosion on the surrounding marshes. Id. at 87. If the government was aware of the effects of erosion on the surrounding marshland and sought to counteract these effects, it may be the case a reasonable landowner would have similarly been aware saltwater from the MRGO was “permanently invad[ing] the private property” and causing the effects on vegetation plaintiffs claim led to the marsh erosion. Boling, 220 F.3d at 1371. Plaintiffs’ claims therefore may have stabilized as early as 1984. See Fallini v. United States, 56 F.3d 1378, 1382 (Fed. Cir. 1995) (noting “[i]t is not necessary that the damages from the alleged taking be complete and fully calculable before the cause of action accrues . . . [so long as] the ‘permanent nature’ of the taking was evident”). By the publication of the 1988 Reconnaissance Report, however, landowners should have been both visually aware of the physical changes occurring to their property and put on notice by the government’s reports on the intrusion of saltwater. Plaintiffs’ takings theory is based on saltwater intrusion from the MRGO leading to increased erosion of plaintiffs’ land. Am. Compl. at ¶ 31. By 1988, publicly available reports and studies made clear “[e]rosion and disintegration of the banks of the MR-GO has created many additional routes for saltwater to intrude into formerly less saline interior marshes” and therefore “salinity in the marshes has increased significantly” over the prior 20 years. 1988 Reconnaissance Report at 27. The report concluded “[s]altwater intrusion . . . contributes significantly to marsh loss in the study area.” Id. 87 Between 1960 and 2000, brackish marsh decreased by 6,346 acres, salt marsh increased by 3,018 acres, swamp decreased by 345 acres, and the area of open water increased by 3,835. Id. at 57. - 53 - Based on the evidence currently before the Court, plaintiffs’ claims likely stabilized at some point between 1984, when the Corps published the Louisiana Coastal Area, Louisiana Land Loss, and Marsh report noting the value of beneficial dredge materials in creating thousands of acres of marshland, and 1988, when the government published the 1988 Reconnaissance Report noting the significant increase in salinity and corresponding erosion in the marshlands of Category Six. Therefore, for the purposes of the cross-motion for summary judgment, absent justifiable uncertainty the six-year statute of limitations period for plaintiffs’ claims related to the marshland of Category Six expired in 1994. See Applegate, 25 F.3d at 1583. 2. Justifiable Uncertainty For landowners to be “justifiably uncertain” as to the permanency of the alleged taking, the “question is whether the ‘predictability [and permanence] of the extent of damage to the [plaintiffs’] land’ was made justifiably uncertain by the Corps’ mitigation efforts.” Banks, 314 F.3d at 1309 (citing Applegate, 25 F.3d at 1583). A project aimed at mitigating damages would constitute justifiable uncertainty as to the permanency of the alleged taking, thus tolling the statute of limitations, if it was implemented after the date on which the Court deems plaintiffs alleged taking to have “stabilized.” Id. To determine whether proposed or actual mitigation efforts by the Corps made landowners justifiably uncertain as to the permanency of the alleged takings of marshlands in Category Six and therefore tolled the statute of limitations, the Court twice had plaintiffs provide supplemental briefing listing proposed and completed projects affecting the justifiable uncertainty analysis of Category Six, and the government had opportunity to respond to each. See Order, ECF No. 152; Order, ECF No. 160. All of the projects plaintiffs provided the Court as applicable to the justifiable uncertainty analysis are considered in the Court’s analysis.88 In support of the existence of justifiable uncertainty by the landowners in Category Six, plaintiffs cite in their supplemental papers “projects, including installation of foreshore protection and beneficial use of dredged material in the years 1985–2003, 1992, 1996, and 2000 as shown in the exhibits attached to ECF Doc. 119; Power Point entitled ‘Mississippi Gulf Outlet Studies, Dated April 6, 2004.’” Pls.’ Supp. Paper at 31. Plaintiffs cite the “exhibits attached to ECF Doc. 119” as supporting the justifiable uncertainty analysis, but the single exhibit attached to ECF No. 119 does not contain the quoted material plaintiffs cite. Instead, the only exhibit attached to ECF No. 119 is a document submitted in support of plaintiffs’ motion for partial summary judgment titled “Capitol Hill Hearing Testimony.” See Pls.’ Notice of Filing Ex. Submitted (1) In Opposition to the United States’ Mot. for Summary J. on the Issue of the Timeliness of the Pls.’ Takings Claim and (2) In Support of Pls.’ Cross-Mot. for Summ. J. on the Same Issue, ECF No. 119, Ex. 1 (Capitol Hill Hearing Testimony). Plaintiffs’ list of proposed projects and studies includes the 1998 Coast 2050 report, which proposed a restoration plan implementing a “dedicated delivery of sediment for marsh building” which “could be pumped from adjacent lakes or rivers to crease marsh in several units . . . [and] is projected to create a moderate amount of marsh.” Coast 2050 Report at 87. A landowner need not receive “a legal binding promise or duty or a matter requiring a congressional appropriation” to be justifiably 88 See supra Section XI.A.2. - 54 - uncertain as to the permanency of an alleged taking. Banks, 314 F.3d at 1309. Rather, the “mere promise” of mitigation efforts, “held out by the Corps and repeatedly renewed but never implemented, indicate[s] that ‘the landowners did not know when or if their land would be permanently destroyed.’” Id. (quoting Applegate, 25 F.3d at 1583). “[P]roposals to correct the damage” done to the land put forward by the government can “further complicate[] ascertaining the extent and nature of the consequences” of the physical taking enough to trigger the doctrine of justifiable uncertainty. Applegate, 25 F.3d at 1584. Although plaintiffs failed to provide a correct citation, Exhibit 60 attached to plaintiffs’ reply brief describes five separate beneficial use sites of dredged material in Eloi Bay apparently active at various points between 1985 and 2003.89 In the 1990s, the Corps also began additional plans and projects directed to a primary goal that there should be “no overall net loss of the Nation’s remaining wetlands base . . . .”90 1990 WRDA at § 307(a). By the late 1990s, and stretching into the early 2000s, the Corps continued implementing and planning additional projects to further mitigate any alleged negative effects to the marshlands.91 Following Hurricane Katrina in 2005, additional projects were contemplated and implemented which effected marshland areas of Eloi Bay.92 The multiple examples of dredge material use sites noted in Exhibit 60 (utilized from 1985 to 2003), as well as the various proposed and completed projects in the 1990s and 2000s, all combine to create a multi-decade period where landowners may have been “justifiably uncertain” as to the permanency of alleged takings in Category Six. Banks, 314 F.3d at 1309–10. The evidence available in the record shows plaintiffs’ claims likely stabilized at some point between 1985 and 1988. Viewing the evidence in the light most favorable to the plaintiff, however, stabilization of plaintiffs’ takings claims in Category One occurred by 1988, when the 1988 Reconnaissance Report was published and the physical changes should have been apparent. The Court therefore concludes the evidence before it, read in the light most favorable to plaintiffs, indicates stabilization occurred no later than 1988. To toll the statute of limitations after the claims have stabilized, proposed or completed mitigation efforts by the government 89 Exhibit 60 is a map titled “Beneficial Use Through MRGO O&M Dredging Miles 60 to 20” and depicts beneficial use of dredged material sites both north and south of the MRGO. Pls.’ Reply Br. Opp’n, Ex. 60. Two of the beneficial use of dredged material locations in Category Six include dates of “FY 85 THRU 03.” Id. Two additional locations include dates of “FY 92 & 96.” Id. Lastly, three separate locations include the date “00.” Id. 90 See supra Section VI.b. 91 In 1999, under the 1996 WRDA, the Corps conducted three projects along the MRGO to create 76 acres of wetlands with materials dredged from the channel. See Am. Compl. at ¶ 53. In the 2004 USCAE LCA Ecosystem Restoration study, the Corps warned that the “rate of wetland loss in the area is accelerating” and “rapid action is required to protect the integrity of the southern lake Borgne shoreline and to prevent continued erosion of the MRGO channel banks from ocean going vessel wakes.” Pls.’ Mot. for Partial Summ. J., Ex. 45 at 31 (U.S. Army Corps of Engineers, Louisiana Coastal Area (LCA), Louisiana, Ecosystem Restoration Study (November 2004)). The Corps proposed building 38 miles of rock breakwaters to prevent the merger of the MRGO into Lake Borgne, facilitating wetland creation by using dedicated dredging and or beneficial use of dredged materials behind the breakwaters, and freshwater introduction into the marsh through Mississippi River diversions. Id. at 32. Additionally, in 2004, the Corps presented in a Power Point the Breaux Act Projects, with four projects included in the PED and two constructed projects. Pls.’ Reply Br. Opp’n, Ex. 56 at 46–47 (U.S. Army Corps of Engineers, MRGO Studies). The PED projects included two shoreline protection projects along Lake Borgne and the MRGO with an estimated cost of $45 million to benefit 495 acres of land, and the constructed projects included two hydrologic restoration projects in the same area which cost $2.6 million and benefited 889 acres. Id. 92 See supra Section VI.b. - 55 - must create “justifiable uncertainty about the permanency of the taking,” and plaintiffs must be “aware of [mitigation] plans” during the period of time they were allegedly justifiably uncertain. Boling, 220 F.3d at 1372. The proposed freshwater diversion program explicitly envisioned creating marshlands through a process of reversing the salinity-induced erosion plaintiffs claim effectuated a taking in the first place. The government further proposed and completed various projects involving the beneficial use of dredged materials and construction of foreshore protections in Category Six between 1985 and 2003, as well as additional projects following Hurricane Katrina in 2005. Reading the evidence of proposed and completed mitigation efforts in the light most favorable to the plaintiff, justifiable uncertainty may toll the statute of limitations on plaintiffs’ claims related to the marshlands of Category Six. See id. XII. Analysis of Category Seven – Jean Louis Robin Jean Louis Robin corresponds to geographical “Subunit 23” of Exhibit 1 contained in the 2012 Feasibility Report. See 2012 Feasibility Report at 2-58. Subunit 23 includes Terre Aux Boeufs,93 Lake Eugenie,94 and Biloxi95 properties. See JSR at 2. Similar to Category One, the subunit does not touch the MRGO channel bank but rather is separated from the channel by the MRGO Spoil Bank. See id.; 2012 Feasibility Report at 2-58. The majority of Jean Louis Robin “is [a] continuous land mass composed mostly of brackish to saline marshes, characterized by small lakes, bays, and meandering bayous.” King Report at 35. A. Stabilization Doctrine As discussed in Category One, plaintiffs assert saltwater intrusion from the MRGO caused additional saltwater intrusion into the South Lake Borgne marshlands. See Am. Compl. at ¶ 31. Plaintiffs also propose an alternative, yet related theory as to the nature of the alleged taking, where saltwater intrusion killed the natural vegetation of the marsh, which in turn reduced the volume of root systems and caused erosion. Id. Prior to dredging of the MRGO, Category Seven was primarily composed of brackish and salt marshes.96 After the MRGO opened, the subunit experienced a dramatic decrease in both salt and brackish marsh, which converted primarily from marshland to open water areas.97 As with Category Five and Category Six, Jean Louis Robin opens directly to Chandeleur Sound, and “[t]he western and easternmost portions of this Zone experience the highest rates of erosion due to wave fetch coming in from both Lake Borgne to the west, and that which filters through the 93 The Terra Aux Boeufs property “consists of two sections, Terre aux Boeufs-East, located north of the MRGO, and Terre aux Boeufs-West, located south of the MRGO.” 2018 Mendelssohn Report at 35. The Western portion of the property is in Jean Louis Robin. Id. at 42. 94 For Lake Eugenie, a portion of the Western and Eastern properties are located in Jean Louis Robin. See 2012 Feasibility Report at 2-58 95 A portion of Biloxi East is in Jean Louis Robin. See 2012 Feasibility Report at 2-58. 96 In the 1950s “Jean Louis Robin was mainly brackish (32, 379 acres) and salt (20,571 acres) marsh.” Day Report at 44. 97 From the 1950s to 1960s “there were a dramatic decrease in both brackish (-5,692 acres) and salt (-6,514 acres) marshes.” Id. at 46. From 1960 to 2000, intermediate marsh increased by 12 acres, brackish marsh decreased by 1,435, and salt decreased by 5,796 and water increased by 7,490 acres. Id. at 57. - 56 - bays and lakes to the east. . . . These problems occur on a daily basis and are exacerbated during tropical events.” King Report at 35. Plaintiffs’ claims likely stabilized by at least 1984, when the Caernarvon freshwater diversion project was first proposed. The Caernarvon project was a freshwater diversion which sought to “convert[] many of the marshes in the Breton Sound basin from higher salinity to lower salinity types . . . .” Gov.’s Mot. for Summ. J., Ex. 17 (Assessment of Wetland Habitat Change on Terre Aux Boeufs and Vincent Marshlands Properties Adjacent to The Mississippi River Gulf Outlet (MRGO)) (“2018 Mendelssohn Report”) at 46. As with the Violet Siphon in Category One, planning and construction of the Caernarvon freshwater diversion project may indicate those installing the diversion were aware of the “substantial encroachment” of saltwater onto Category Six property, recognizing the encroachment of saltwater may result in the death of local flora sensitive to salinity changes and eventually lead to greater land erosion without freshwater diversions to counteract these effects.98 See Boling v. United States, 220 F.3d 1365, 1372 (Fed. Cir. 2000) (the stabilization doctrine requires the Court to determine when there was sufficient “substantial encroachment” onto plaintiffs’ land to make plaintiffs aware of the alleged taking). By 1988, however, landowners had sufficient evidence of the substantial encroachment of saltwater onto their land. The 1988 Reconnaissance Report explicitly noted “salinity in the marshes has increased significantly in the last 20 years” and documented a corresponding vegetation and marsh loss in the marshlands surrounding the MRGO. 1988 Reconnaissance Report at 27. In 1988 landowners should have therefore been put on notice of the permanency of their takings claims through both the public statements by the government on saltwater intrusion and corresponding marsh loss, and through the physical effects of the saltwater intrusion documented in the 1988 Reconnaissance Report. In summary, for Category Seven, the evidence in the record indicates “environmental forces . . . substantially and permanently invaded the private property” sufficient for the stabilization doctrine to apply at some point between 1984, when the Caernarvon freshwater diversion project was first planned, and 1988, when the 1988 Reconnaissance Report was published. Boling, 220 F.3d at 1371. Viewing the evidence in the light most favorable to the plaintiff for the purpose of the government’s motion for summary judgment, absent justifiable uncertainty the six-year statute of limitations period for plaintiffs’ claims related to the marshland of Category Two expired in 1994. See Applegate v. United States, 25 F.3d 1579, 1583 (Fed. Cir. 1994). B. Justifiable Uncertainty For landowners to be “justifiably uncertain” as to the permanency of the alleged taking, the “question is whether the ‘predictability [and permanence] of the extent of damage to the [plaintiffs’] land’ was made justifiably uncertain by the Corps’ mitigation efforts.” Banks v. United States. 314 F.3d 1304, 1309 (Fed. Cir. 2003). A project aimed at mitigating damages would constitute justifiable uncertainty as to the permanency of the alleged taking, thus tolling 98 The government’s 1988 Reconnaissance Report in fact explicitly concluded the increased salinity levels contributed to the reduction of “the amount of three-cornered grass” growing in the local marshlands and “[s]altwater intrusion . . . contributes significantly to marsh loss in the study area.” 1988 Reconnaissance Report at 27. - 57 - the statute of limitations, if it was implemented after the date on which the Court deems plaintiffs alleged taking to have “stabilized.” Id. To determine whether proposed or actual mitigation efforts by the Corps made landowners justifiably uncertain as to the permanency of the alleged takings in Category Seven and therefore tolled the statute of limitations, the Court twice had plaintiffs provide supplemental briefing listing proposed and completed projects affecting the justifiable uncertainty analysis of Category Seven, and the government had an opportunity to respond to each. See Order, ECF No. 152; Order, ECF No. 160. All of the projects plaintiffs provided the Court as applicable to the justifiable uncertainty analysis are considered in the Court’s analysis.99 Plaintiffs’ supplemental papers point to the completed Caernarvon freshwater diversion project, a 1984 evaluation report, and a 1993 Environmental Impact Statement as applicable projects to a justifiable uncertainty analysis. See Pls.’ Supp. Paper at 15–24. The Caernarvon freshwater diversion structure was first proposed in 1984, construction began in 1988, and it was completed in 1991.100 See Pls.’ Mot. for Partial Summ. J., Ex. 42 at 5 (1994 MRGO Bank Erosion Reconnaissance Report). This diversion structure continues to operate today. See Pls.’ Supp Paper at 24. The 1993 Louisiana Coastal Wetlands Restoration Plan emphasized “management of the Caernarvon Freshwater Diversion Structure’s outfall . . . is vital to the restoration of [the surrounding marshlands] because such projects will help to maintain and restore the hydrology of the basin.” See Pls.’ Supp. Paper at 23. Dr. Mendelssohn’s report similarly noted a decrease in the salinity of Category Seven from 1988 to 1997, “with brackish marsh increasing and saline marsh decreasing.” 2018 Mendelssohn Report at 7. Dr. Mendelssohn attributed “[t]he substantial increase in brackish marsh” as “due to the opening of the Caernarvon Freshwater Diversion in 1991.” Id. at 7–8. As with Category One, plaintiffs’ theory of takings is based on saltwater intrusion increasing the salinity of the marshland, which allegedly killed the natural vegetation of the marsh and led to erosion of soil no longer held in place by root systems. Am. Compl. at ¶ 31. A decrease in the salinity of marshlands following the construction of the freshwater diversion system could indicate to landowners in Category One the Caernarvon Diversion is both providing sediment dispersals through freshwater diversions and lowering the salinity of the surrounding marshlands to the point of dramatically slowing the rate of erosion. Applegate, 25 F.3d at 1583. As additional evidence of this, the Mendelssohn report explicitly notes Terra Aux Boeufs experienced a freshening effect from 1988 to 1997, consistent with the operation of the diversion.101 During this time the Corps 99 Plaintiffs’ 15 June 2020 supplemental paper listed the following completed or proposed items applying to a justifiable uncertainty analysis for Category Seven: A 1994 USACE bank erosion report; the Louisiana Coastal Wetlands Restoration Plan of 1993; the 1988 Reconnaissance Report; the Mississippi River Gulf Outlet Ecosystem Restoration Plan’s Final Feasibility Report; and projects related to the beneficial use of dredged materials. See Pls.’ Paper at 7–8. Plaintiffs’ 30 June 2020 supplemental paper listed the following completed or proposed items applying to a justifiable uncertainty analysis for Category Seven: Feasibility reports recommending freshwater diversions into the region; studies, proposals, and reports contained in the 1984 Initial Evaluation Report; and the construction and operation of the Caernarvon freshwater diversion project. Pls.’ Supp. Paper at 15–24. 100 The Corps prepared a report titled “Louisiana Coastal Area, Freshwater Diversion to Bataria and Breton Sound Basins” in September 1984. Pls.’ Mot. for Partial Summ. J., Ex. 42 at 5 (1994 MRGO Bank Erosion Reconnaissance Report). This report “recommended diverting Mississippi River water into the Breton Sound Basin near Caernarvon . . . to enhance habitat conditions and improve fish and wildlife resources.” Id. The freshwater diversions “would reduce land loss and save about 99,200 acres of marsh.” Id. 101 “The substantial increase in brackish marsh from 1988 to 1997 . . . was likely due to the opening of the Caernarvon freshwater diversion that converted many of the marshes in the Breton Sound basin from higher salinity - 58 - additionally undertook projects in the area for the beneficial use of dredged material,102 consistent with the Corps’ goal of “no overall net loss of the Nation’s remaining wetlands base.” 1990 WRDA at § 307(a).103 Viewing the evidence in the light most favorable to plaintiffs, stabilization of the plaintiffs’ takings claims in Category One occurred by 1988, when the 1988 Reconnaissance Report was published and the physical changes should have been apparent. The Court therefore concludes the evidence before it, read in the light most favorable to the plaintiff, indicates stabilization occurred no later than 1988. To toll the statute of limitations after the claims have stabilized, proposed or completed mitigation efforts by the government must create “justifiable uncertainty about the permanency of the taking,” and plaintiffs must be “aware of [mitigation] plans” during the period of time they were allegedly justifiably uncertain. Boling, 220 F.3d at 1372. The Caernarvon freshwater diversion project, proposed in 1984 and completed in 1988, had a dramatic freshening effect on the surrounding area and continues to operate. The Corps further proposed additional beneficial use dredging projects related to Category Seven. Reading the evidence of the proposed and completed mitigation efforts in the light most favorable to the plaintiffs, justifiable uncertainty may toll the statute of limitations on plaintiffs’ claims related to Category Seven. See id. XIII. Analysis of Category Eight – Lake Borgne In the 8 May 2020 joint status report dividing the properties into various subunits for the purposes of stabilization and justifiable uncertainty analyses, both parties agreed to divide plaintiffs’ property into categories one through seven. See JSR at 1–2. Plaintiffs, however, sought to also add an eighth subunit—Lake Borgne. Id. at 3–6. Lake Borgne corresponds to geographical “Subunit 26” of Exhibit 1 contained in the 2012 Feasibility Report. See 2012 Feasibility Report at 2-58. At oral argument, the government noted any land which would have eroded into Lake Borgne was originally part of one of the other seven subunits agreed to by the parties and argued such land should be calculated in a takings analysis as land lost from one of the other subunits. See ECF No. 159 at 4:51:30–4:52:05 (recording of oral argument). After oral argument, and in all supplemental briefing regarding projects that may apply to a justifiable uncertainty analysis for each proposed subsection, plaintiffs did not include any projects specifically directed to the proposed Category Eight. See Pls.’ Supp. Paper; Gov.’s Resp. to Pls.’ Supp. Paper. As the government noted at oral argument, plaintiffs’ claims all relate to land allegedly taken from one of the seven categories, rather than land existing in Lake Borgne prior to the construction of the MRGO. See 2012 Feasibility Report at 2-58. While plaintiffs did not explicitly agree to withdraw their request for an eighth subunit, they did not object at oral to lower salinity types . . . . This freshening affect was most apparent in the western half of Breton Sound, where the 1988-brackish marshes transitioned to intermediate marshes in 1997.” 2018 Mendelssohn Report at 46. 102 In 1998, EA #269 and EA #269-A detailed the Corps’ establishment of additional disposal areas “from Miles 36.5 to 32 and Miles 49.0 to 46.5” and emphasized how the material would be placed into the disposal sites “in a manner conducive to wetland development, creating and/or restoring wetlands each cycle.” Pls.’ Mot. for Partial Summ. J., Ex. 25 at 1 (EA # 269 and EA # 269-A: South of Lake Borgne Additional Disposal Areas). 103 See supra Section VI.b. - 59 - argument to the government’s characterization of plaintiffs’ claims as addressing only land originating from one of the seven categories already discussed and plaintiffs’ supplemental briefing following oral argument on projects related to the Court’s justifiable uncertainty analysis does not include any projects specifically affecting proposed Category Eight. See ECF No. 159 at 4:51:30–4:52:05 (recording of oral argument); Pls.’ Supp. Paper. Accordingly, the Court will not separately consider a distinct category of land now covered by Lake Borgne in its analysis, but rather agrees with the government’s summary that all land proposed by plaintiffs to be included in Category Eight has already been considered in one of the previous seven categories. See supra Sections VI–XII. XIV. Summary of the Court’s Conclusions on Each Category of Land The following chart summarizes the application of the stabilization and justifiable uncertainty doctrines to Categories One through Seven. The exact boundary lines between the individual subunits remain undefined. As this court acknowledged in past physical takings cases, such “issues . . . cannot be addressed without further factual development” for claims that “turn[] on disputed issues of material fact” are not ripe for summary judgment. Pellegrini v. United States, 132 Fed. Cl. 64, 73 (2017). While the Court sets out to resolve the timeliness of claims for the seven defined categories of land, the Court leaves for the parties or further proceedings to determine the applicability of this decision to various plaintiffs and their specific parcels of land. Category Range of Time the Range of Time The Court’s ruling Stabilization Landowners May on the cross-motions Doctrine May Apply Have Been for summary Under the Evidence Potentially judgment Before the Court Justifiably Uncertain Category 1 (Central 1978–1988 1978–1983; 1990– DENYING Wetlands) 2004; 2006–2012 government’s motion for summary judgment and DENYING plaintiffs’ motion for summary judgment Category 2 (South 1983–1988 1988–2012 DENYING Lake Borgne)- government’s motion Channel for summary judgment and DENYING plaintiffs’ motion for summary judgment Category 2 (South 1984–1988 1992–2012 DENYING Lake Borgne)- government’s motion Marshlands for summary judgment and - 60 - DENYING plaintiffs’ motion for summary judgment Category 3 (MRGO 1983–1988 1983–2012 DENYING Spoil Bank) government’s motion for summary judgment and DENYING plaintiffs’ motion for summary judgment Category 4 (Biloxi 1988 1993–2012 DENYING Marshes Interior) government’s motion for summary judgment and DENYING plaintiffs’ motion for summary judgment Category 5 (Biloxi 1988 1988–1996 GRANTING Marshes Exterior) government’s motion for summary judgment and DENYING plaintiffs’ motion for summary judgment Category 6 (Eloi 1985–1988 1988–2012 DENYING Bay)- Channel government’s motion for summary judgment and DENYING plaintiffs’ motion for summary judgment Category 6 (Eloi 1984–1988 1985–2012 DENYING Bay)- Marshland government’s motion for summary judgment and DENYING plaintiffs’ motion for summary judgment Category 7 (Jean 1984–1988 1984–2012 DENYING Louis Robin) government’s motion for summary judgment and DENYING plaintiffs’ motion for summary judgment - 61 - The six-year statute of limitations established under the Tucker Act “is an explicit condition of the government’s waiver of sovereign immunity and, as a matter of law, jurisdictional.” Prakhin v. United States, 131 Fed. Cl. 706, 713(2017) (citing John R. Sand & Gravel Co. v. United States, 552 U.S. 130, 139 (2008)). “Because the statute of limitations is jurisdictional, the plaintiff bears the burden of proof.” Petro-Hunt, L.L.C. v. United States, 862 F.3d 1370, 1378 (Fed. Cir. 2017). The government argues “substantially all of the habitat change [p]laintiffs complain of, and thousands of acres of land loss had occurred by at least 1988,” and, therefore, “[p]laintiffs’ claims accrued by at least 1988 and they were obligated to file suit by at least 1994.” Gov’t Mot. for Summ. J. at 26. Plaintiffs, meanwhile, argue the “gradual physical processes that have eroded and continue to erode plaintiffs’ properties” either “to this date have not stabilized” or, if the claims have stabilized, “stabilization did not occur until July 9, 2009, when the MRGO was finally physically closed . . . .” Pls.’ Mot. for Partial Summ. J., Ex. 1 at 2. Viewing the evidence before the Court in favor of the non-moving party for the purpose of each of the cross-motions for summary judgment, stabilization of each of plaintiffs’ claims occurred at some point in a range of time starting in the late 1970s or early 1980s and ending in 1988. See supra. This in turn means the statute of limitations on each claim ran until 1994 or earlier, barring justifiable uncertainty. Applegate, 25 F.3d at 1583. To establish justifiable uncertainty tolling the statute of limitations for a takings claim, plaintiffs must demonstrate “the landowners did not know when or if their land would be permanently destroyed.” Applegate, 25 F.3d at 1582 (emphasis added). This justifiable uncertainty as to “whether ‘the predictability [and permanence] of the extent of damage to the [plaintiffs’] land’” must be caused by the government’s “mitigation efforts.” Banks, 314 F.3d at 1309. Further, the Federal Circuit has made clear there can be no justifiable uncertainty when “the plaintiffs . . . were not aware of [mitigation] plans until after they filed [the] lawsuit.” Boling, 220 F.3d at 1372. The Court must look to what the particular landowners knew during the period of time plaintiffs claim the statute of limitations was tolled to determine whether or not the landowners were actually justifiably uncertain as to “when or if their land would be permanently destroyed.” Applegate, 25 F.3d at 1582. Based on the range of possible stabilization dates, and examining the totality of the government’s actions in the form of previously completed projects and numerous studies, reports, legislation, and funding appropriated for future projects in the light most favorable to the non-moving party, the Court cannot definitively say whether or not the government’s actions created justifiable uncertainty as to the permanency of the alleged government taking beyond the specificity in the ranges noted supra. Matsushita Elec. Indus. Co., Ltd. v. Zenith Radio Corp., 475 U.S. 574, 587–88 (1986) (noting the Court must draw all inferences “in the light most favorable to the party opposing the motion.”). The ultimate question in a justifiable uncertainty analysis is whether “the landowners [did or] did not know when or if their land would be permanently destroyed.” Banks, 314 F.3d at 1309 (quoting Applegate, 25 F.3d at 1583) (quotation marks removed) (emphasis added). For Categories One, Two, Three, Four, Six, and Seven of land, plaintiffs have been able to establish justifiable uncertainty may toll the statute of limitations sufficient to overcome the government’s motion for summary judgment. See supra Sections VI, VII, VIII, IX, XI, and XII. In each section, plaintiffs have shown proposed or completed projects which, viewing the - 62 - evidence in the light most favorable to the plaintiffs, left landowners justifiably uncertain as to the permanency of the alleged taking. See supra. While the record contains various proposed and completed projects affecting each category of land, however, it does not foreclose the possibility a landowner did not have actual knowledge of enough of the proposed and completed mitigation projects to be justifiably uncertain as to the permanency of the alleged taking. Applegate, 25 F.3d at 1583 (finding “the landowners remain justifiably uncertain about the permanency of the erosion and the taking” because of the government’s promise to mitigate). At any future trial the Court will have to closely examine the specific knowledge landowners had related to the proposed and completed mitigation actions contained in the record and whether these actions resulted in justifiable uncertainty on the part of the landowners as to the permanency of the government’s taking. See, e.g., Henderson County Drainage Dist. No. 3 v. United States, 60 Fed. Cl. 748 (2004) (relying on witness and expert testimony related to documents in the record presented at trial in part to rule on whether plaintiffs’ takings claims related to the operation and maintenance of a navigation channel was justifiably delayed); Kingsport Horizontal Property Regime v. United States, 53 Fed. Cl. 556 (2002) (utilizing expert and witness testimony, as well as surveys entered into the record, presented to the court during a trial to determine whether the stabilization doctrine applied to different tracts of land). Without an examination of what the specific landowners knew and how this knowledge affected their potential uncertainty regarding the permanency of any taking, the Court cannot say whether the mitigation projects presented by plaintiffs as applicable to the justifiable uncertainty doctrine actually tolled the statute of limitations after the takings claims stabilized. XV. Conclusion In each of the seven categories of property considered by the Court, and viewing the evidence in the light most favorable to the non-moving party for each summary judgment motion, the stabilization doctrine started the statute of limitations on plaintiffs’ claims during time ranges varying by category, but in each case no later than 1988. Reviewing evidence in the light most favorable to plaintiff, the proposed and completed projects in Categories One, Two, Three, Four, Six, and Seven, however, result in landowners who were, or may have been, “justifiably uncertain” as to the permanency of alleged taking and therefore may have tolled the statute of limitations. The Court cannot definitively say, however, landowners were justifiably uncertain without further evidence regarding what landowners knew about the proposed and completed projects, and how this relates to any uncertainty as to the permanency of the alleged takings. Accordingly, the Court GRANTS-IN-PART and DENIES-IN-PART the government’s motion for summary judgment. Further, the Court DENIES plaintiffs’ cross- motion for summary judgment. The parties shall meet and confer and submit a joint status report proposing a timeline for further proceedings consistent with this opinion on or before 19 February 2021. The joint status report shall include: (1) whether the parties intend to submit motions to resolve plaintiffs’ contractual claims, or address those claims at trial; (2) whether the parties will request further discovery before trial; and (3) scheduling suggestions to begin planning trial proceedings including respective positions on bifurcating any claims or testimony, location for trial proceedings, and time limits for trial presentation and testimony. - 63 - IT IS SO ORDERED. s/ Ryan T. Holte RYAN T. HOLTE Judge - 64 -