South Carolina              
Administrative Law Court
Edgar A. Brown building 1205 Pendleton St., Suite 224 Columbia, SC 29201 Voice: (803) 734-0550

SC Administrative Law Court Decisions

CAPTION:
League of Women Voters of Georgetown, et al vs. SCDHEC, et al

AGENCY:
South Carolina Department of Health & Environmental Control

PARTIES:
Petitioners:
League of Women Voters of Georgetown and South Carolina Coastal Conservation League

Respondents:
South Carolina Department of Health & Environmental Control and Wedgefield
Plantation Association
 
DOCKET NUMBER:
07-ALJ-07-0529-CC

APPEARANCES:
Amy E. Armstrong, Esq. and James S. Chandler, Jr., Esq., for Petitioners

Elizabeth A. Dieck, Esq., for Respondent South Carolina Department of Health and Environmental Control

Mary D. Shahid, Esq. for Respondent, Wedgefield Plantation Association
 

ORDERS:

FINAL ORDER AND DECISION

STATEMENT OF THE CASE

This matter is before the Administrative Law Court (ALC or Court) upon Petitioners’ request for a contested case hearing pursuant to the Administrative Procedures Act to challenge the Final Agency Decision of the Board of the South Carolina Department of Health and Environmental Control (DHEC or Department), issued October 11, 2007, of a 401 water quality certification and coastal zone consistency certification, provided in response to a permit application pending before the United States Army Corps of Engineers (Corps), P/N # 2006-3476-4IV. The permit application, which was submitted by Respondent Wedgefield Plantation Association (WPA), seeks authorization to perform maintenance dredging in the existing canals within the Wedgefield Plantation subdivision in Georgetown County, South Carolina, and to dispose of the dredged material in an area identified by WPA as an existing disposal basin.

Petitioners are not challenging the authorization to dredge the canal system at Wedgefield Plantation, but are contesting the certification of use of the area identified as “existing disposal basin” for dredge disposal, since that area is characterized as a freshwater wetland. Specifically, Petitioners argue that WPA’s proposal to place dredged spoil material into a previously-constructed spoil disposal basin that is located within a freshwater wetland violates the S.C. Pollution Control Act, S.C. Code Ann. §48-39-10 (Supp. 2006), the water quality certification regulations, and the Coastal Zone Management Program.[1]

Petitioners also filed a Motion for Summary Judgment related to WPA’s efforts in 2003 to obtain a permit for dredging the canals and for spoil disposal. The earlier application was denied by the Department. Petitioners sought review of that denial before the ALC, in a contested case involving the same parties, Docket No. 04-ALJ-07-0351-CC. However, the action was dismissed for lack of jurisdiction based upon WPA’s failure to timely file a request for a contested case. Petitioners thus assert that the certification of the disposal of the dredged spoil material in this case is barred by res judicata. Additionally, Respondent WPA filed a Motion to Dismiss based on the timeliness of Petitioners’ request for review. Those Motions are addressed herein.

After notice to the parties, a contested case hearing on the merits of this matter was held on August 25 and 26, 2008, at the Administrative Law Court in Columbia, South Carolina.

FINDINGS OF FACTS

Having observed the witnesses and exhibits presented at the hearing and taking into consideration the burden of persuasion and the credibility of the witnesses, I make the following findings of fact by a preponderance of evidence:

General Findings

The Wedgefield Plantation subdivision is located adjacent to the Black River in Georgetown County, South Carolina. Wedgefield Plantation was initially developed in 1970. There are approximately 580 home sites, including 81 lots that front the canal system. In its permit application, WPA seeks authorization to perform maintenance dredging of 99,400 cubic yards of material in the existing canals within the Wedgefield subdivision, and to dispose of the dredged material in an area identified as an existing 12.8 acre spoil disposal basin.

Permitting Background

The history of dredging operations at Wedgefield Plantation dates back to the 1970’s when the subdivision was first developed. The Department of the Army, through the Corps of Engineers, issued a permit dated July 27, 1970, authorizing the dredging of canals in abandoned rice fields at Wedgefield Plantation. The drawings attached to the permit indicate dredging proposed in a series of finger canals, and a main canal that connected to the Black River. The drawings also include the notation that “[a]pproximately 265,000 cubic yards to be dredged which will be placed in the disposal areas as shown behind a retention embankment.” There was no specific authorization in the 1970 permit for construction of a spoil disposal basin.

Over time the canals began silting in, and in 1982 Wedgefield Plantation Association applied for a new permit for authorization to conduct maintenance dredging of the existing canals. This application triggered comment from State and Federal resource agencies.[2] In their initial comments, the State and Federal resource agencies objected to the permit application. In response, Wedgefield modified the permit application. The modifications depicted a reduction in the size of the proposed spoil disposal area from 22 acres to 9.2 acres. They also revealed multiple 20' wide cuts to be made in an existing adjacent impoundment that would open that impounded area to exchange with the Black River, along with the installation of pipes under an existing causeway identified as Boat House Road. In addition, Wedgefield reduced the depth of the canals. Based on these modifications, the state and federal resource agencies reviewing the application withdrew all objections.

The Corps issued a permit to Wedgefield Plantation on May 13, 1983, authorizing maintenance dredging of the existing canals. The permit included a “Statement of Findings” from the Corps’ District Engineer that federal agency objections were removed “provided certain modifications were made to the project and that the Federal permit incorporate mitigation plans for wetland losses that were discussed with the applicant during the processing of this application.” These above-mentioned modifications included reducing the size of the dredged material disposal area to avoid major filling of wetland areas and reducing the depth of all finger canals from 8’ to 6’ below mean low water. The mitigation plan consisted of breaching an adjacent rice field’s embankments at several locations in order to allow a daily exchange of water between the Black River and the rice field.

On August 8, 2003, Wedgefield Plantation Homeowners Association again submitted a permit application to the Corps of Engineers for maintenance dredging and spoil disposal. The application depicted a 14.92 acre “proposed confined disposal basin” described as “wetlands proposed to be impacted.” The permit drawings depicted depths of dredging in most locations as -8 MLW. After reviewing the application, the Department issued a “Notice of Proposed Decision” on July 28, 2004, in which it denied the water quality certification and coastal zone consistency certification. In that decision, the Department determined that using the wetlands for spoil disposal was not the least damaging alternative and that it would result in unnecessary, permanent impacts. The Department further found that rather than using the proposed disposal area, “[a]n existing intact spoil disposal area or a contained upland disposal area should be used for this type of project.” WPA filed a request with the ALC for review of the Department’s denial, but that request was ultimately dismissed because the request was made after the 30-day deadline for filing set forth in ALC Rule 11.[3]

On May 31, 2006, WPA filed the application at issue in this case with the Corps of Engineers seeking authorization to perform maintenance dredging and to deposit spoil material in the existing spoil disposal basin. That application was subsequently revised on November 2, 2006, to provide an alternative analysis related to spoil disposal methods. The application differed from the 2003 application in that:

·                     the size of the “existing confined disposal basin” was shown as 12.8 acres;

·                     the depth of dredging was adjusted in one section of the canals;

·                     the width of the dredge cut was reduced to allow for a 10’ wide buffer on either side of the canal; and

·                     the shape of the dredge cut was altered from a box cut to a “v” shaped cut.

The Department concluded that the permit application was consistent with the S.C. Coastal Zone Management Program, and it issued its 401 water quality certification on July 13, 2007. More specifically, the Department determined that the area that it had previously concluded was not a confined disposal area was indeed a confined disposal area that was appropriate to receive the spoils from the proposed dredging.

On July 30, 2007, Petitioners sought review by the DHEC Board. The Board conducted a final review conference on September 7, 2007 and subsequently concluded that “Department staff properly evaluated applicable legal requirements in issuing the permit, 401 water quality certification and coastal zone consistency determination under review.”

Dredging

WPA seeks approval to “dredge 99,400 cubic yards of material from two entrance canals and portions of the adjacent canal system.” The Black River’s considerable sediment, and sediment transport from the River into the canals is the primary cause of siltation in the canals. As a result, the canals have gradually silted in since the dredging operation that occurred following the issuance of the 1983 permit.[4] In some instances there is no evidence of a channel, but only of a large flat expanse of mud. WPA members who own property along the canals can currently navigate from their docks within an hour on either side of high tide. This allows for only a two-hour window of opportunity for boating. If property owners boat longer than two hours, they must stay out eleven hours, or until the next high tide, before they can return to their docks. There is also very little wildlife or fishery resources in the canals as a result of the decreased water depths.

Therefore, the canals are no longer navigable at low tide and the navigability at high tide has been greatly reduced. It also appears that following a maintenance dredging event the canals are useable for approximately fifteen to twenty years. Accordingly, if WPA is not able to perform maintenance dredging, the canals will, in time, be rendered non-navigable at any tidal stage. Furthermore, dredging will allow the return of aquatic life that once inhabited the canals.

Spoil Disposal Area

WPA proposes to place the spoil material from the above-referenced dredging in an adjacent 12.8 acre disposal basin.[5] The existing 12.8 acre disposal area[6] that WPA proposes to utilize is a “confined” or “contained” area. More specifically, the disposal area is surrounded by an intact dike, or embankment, separating the disposal area from the Black River, surrounding marshes, and the main canal. The embankment is at a significantly higher elevation than the area inside the embankment and can be described as “high ground.” The spoil disposal area also includes water control structures such as a “flash board riser” and an “overflow pipe” which are designed to prevent water from the Black River and surrounding marshes from flowing into the disposal area and to only allow water to flow out of the area.[7] These structures, described as the return water discharge, were required as a condition of the 401 water quality certification of the 1983 permit. Therefore, the embankment and water control structures prevent any exchange between the area inside the embankment and the surrounding marshes, the Black River, and the main canal. Any outfall from those pipes would be extremely limited under present conditions.

Since the proposed spoil disposal area is a completely confined or contained area, the proposed activity in WPA’s permit application will have no effect on the Black River and surrounding marshes. This finding is significant in light of the permitting history of this site. The Department previously denied the 2003 coastal zone consistency certification and 401 water quality certification based on the assumption that the embankment surrounding the spoil disposal area was breached and that there was a connection between the spoil disposal area and the surrounding marshes and the Black River. Because of this assumption, the Department concluded that allowing the applicant to repair the existing embankment and utilize the area for spoil disposal would adversely affect water quality in the Black River. That adverse impact would occur because the repair of the embankment would cut off the spoil disposal area from the Black River and thus eliminate the functions and values of the area to the ecosystem of the Black River. However, in reality, those functions and values did not exist. The Department’s staff had erroneously assumed that the embankment had not been maintained. Thus, its previous conclusion that the 2003 permit application would have had an adverse effect on the Black River and surrounding marshes was marred by its erroneous assumption that the embankment was not intact. Had the Department’s staff been made aware of the actual condition of the embankment in 2003, it is likely that the certifications would have been issued.

Environmental Impact of Disposal in the Basin

The area inside the embankment is a freshwater wetland. Phragmites grass dominates the ecology of the wetland within the spoil area, and Phragmites grass is a productive component of wetland ecosystems. If spoil material is pumped onto the proposed disposal area, it will result in the elimination of the wetlands in the 12.8 acre disposal area. The wetlands in this area would be replaced with an upland ecosystem, which is not as productive as a marsh ecosystem. Nevertheless, as explained below, the use of a freshwater wetland area as a spoil disposal area is not prohibited under the S.C. Coastal Management Program.

Mitigation

The mitigation accomplished through the 1983 permitting action and the previous use of the area at issue in this case are significant considerations in evaluating the feasibility of avoiding the placement of dredged material in this area. See S.C. Coastal Management Program p. III-57 (“[t]o the maximum extent feasible, dredged material must not be placed on high value natural habitats such as salt, brackish or freshwater wetland”). In 1983, Wedgefield Plantation sought approval to construct and maintain a 22 acre spoil disposal site. The proposed spoil disposal area, however, consisted of wetlands.[8] As is clear from the Corps’ Statement of Findings appended to the 1983 permit, Wedgefield Plantation agreed to reduce wetland impacts by significantly reducing the size of the spoil disposal area. It also agreed to a mitigation plan to address all of the wetland losses associated with the project. OCRM, through its certification of the 1983 permit, concluded that the mitigation adequately addressed the loss.

The 1983 mitigation continues to benefit the surrounding area and functions as compensation for the losses associated with the creation, maintenance, and continued use of the spoil disposal area. The 20' breaches that were created in the adjacent impoundment greatly enhanced the tidal exchange between the Black River and the adjoining marshes and significantly enhanced the exchange of nutrients. Moreover, it also notable that the same area that was certified in 1983 as consistent with the Coastal Management Program was certified under the same policies as applied to this permit application. That certification resulted in the construction of the very spoil disposal basin at issue in this case.

Aquatic Ecosystem and Water Quality Impacts

While the placement of spoil material from dredging will eliminate the wetlands inside the disposal area, it will not permanently alter the aquatic ecosystem in the vicinity of the project such that its functions and values are eliminated or impaired. Here, the vicinity of the project is not limited to the spoil disposal area, but is rather the canals in Wedgefield Plantation, the marshes surrounding the Black River, and the Black River. Since the spoil disposal area is separated from the Black River and the surrounding marshes, it will not impact the adjacent aquatic ecosystem. Furthermore, the removal of the functions and values of the wetlands within the spoil disposal area will not have an adverse impact on water quality in the adjacent aquatic ecosystem.

Feasible Alternatives

Nevertheless, in accordance with the regulations, several options were presented as feasible alternatives to the proposed project. Those options included:

·                     dewatering and hauling sediment off site for disposal, including rapid dewatering;

·                     use of geotextile tubes as bulkheading along the canals; and

·                     taking no action to preserve the navigation in the Wedgefield Plantation canals and using the existing community dock and boat ramp as access to the Black River.

Dewatering can be accomplished through different methods. The cost of the dewatering alternatives ranged from five to seven times greater than the cost of disposal in the 12.8 acre spoil site. Moreover, these alternatives would require WPA to purchase an upland site for disposal, or to find an available landfill to accept a significant amount of fill material. The dewatering alternatives are thus too costly in comparison to the impacts of using the spoil site.[9] The geotextile tubes alternative also involves hauling and disposal off-site and thus is too costly in comparison to the impacts of using the spoil site.[10] It is also notable that the Petitioners presented no evidence to demonstrate that either dewatering or use of the geotextile tubes is feasible. Furthermore, input from other agencies should be evaluated in determining feasibility. In that regard, neither the S.C. Department of Natural Resources nor the U.S. Fish and Wildlife Service has commented on the permit application or objected to the project.

Additionally, use of the existing community dock and boat ramp is not an acceptable alternative. While this alternative provides some form of water access, it certainly does not address the condition of the canal system in Wedgefield Plantation. Moreover, the Court must consider the substantial number of Wedgefield Plantation owners that would be required to use the area and the significant impact that loss of the use of the canals would have upon WPA and the environment. Finally, this Court cannot overlook the fact that the 12.8 acre disposal site was constructed for the exclusive purpose of maintaining the canals at Wedgefield Plantation and has been specifically used for this purpose. In fact, compensation for the wetland losses at the 12.8 acre spoil site disposal has already been considered, approved and implemented. Therefore, there is no identified feasible alternative to this project’s proposed use of the existing confined disposal facility for spoil disposal.

CONCLUSIONS OF LAW

This Court has subject matter jurisdiction in this case pursuant to S.C. Code Ann. § 1-23-600(A) (as amended by 2008 S.C. Act No. 334) and S.C. Code Ann. § 44-1-60(F)(2) (2008). The hearing before the ALC is a contested case hearing pursuant to the APA and is heard de novo. Marlboro Park Hosp. v. S.C. Dep’t of Health and Envtl. Control, 358 S.C. 573, 595 S.E.2d 851 (2004). The proper standard of proof to be applied is a preponderance of the evidence. Anonymous (M-156-90) v. State Bd. of Med. Examiners, 329 S.C. 371, 496 S.E.2d 17 (1998); National Health Corp. v. Dep’t of Health and Envtl. Control, 298 S.C. 373, 380 S.E.2d 841 (Ct. App. 1989). Furthermore, the burden of proof is upon the party asserting the affirmative of an issue and, therefore, Petitioners bears the burden in this case of proving that the agency decision was in error under the statutory and regulatory standards. Leventis v. Dep’t of Health and Envtl. Control, 340 S.C. 118, 530 S.E.2d 643 (Ct. App. 2000).

Permit Application Process

This contested case was initiated by a permit application pending before the Corps. In response to this permit application, the Corps and the Department issued a “Joint Public Notice” pursuant to Section 10 of the Rivers and Harbors Act of 1899 (33 U.S.C. §403), Sections 401 and 404 of the Clean Water Act (33 U.S.C. §1344), the South Carolina Coastal Zone Management Act (S.C. Code Ann. §48-39-10 et. seq. (Supp. 2006)), and the South Carolina Construction in Navigable Waters Permit Program (23 S.C. Code Ann. Reg. 19-450, et seq. (Supp. 2006)). The proposed activity of maintenance dredging and spoil disposal triggered multiple reviews by the Corps and the Department.

The Corps’ permitting authority derives from the Clean Water Act, 33 U.S.C. §1344. In accordance with 33 U.S.C. §1344(a):

The Secretary[11] may issue permits, after notice and opportunity for public hearings for the discharge of dredged or fill material into the navigable waters at specified disposal sites. Not later than the fifteenth day after the date an applicant submits all the information required to complete an application for a permit under this subsection, the Secretary shall publish the notice required by this subsection.

The Department’s Bureau of Water also reviews these permit applications pursuant to 33 U.S.C. §1341(a):

Any applicant for a Federal license or permit to conduct any activity including, but not limited to, the construction or operation of facilities, which may result in any discharge into the navigable waters, shall provide the licensing or permitting agency a certification from the State in which the discharge originates or will originate …that such discharge will comply with the applicable provisions of … this Act.

The Department’s review of a “401 water quality certification,” is governed by 25A S.C. Code Reg. 61-101(A)(2). Regulation 61-101(A)(2) provides that “[a]ny applicant for a Federal license or permit to conduct any activity which during construction or operation may result in any discharge to navigable waters is required by Federal law to first obtain a certification from the Department.”

In addition to its water quality certification review, the Department must also determine whether to issue a permit authorizing WPA’s activities in the State’s navigable waters. The Department has promulgated regulations governing the review of the State’s Navigable Waters permits in 23 S.C. Code Ann. Reg. 19-450, et seq. Nonetheless, when an applicant submits a permit application seeking both a 401 water quality certification and a permit for construction in State navigable waters, “the review for the water quality certification will consider issues of that permit and the Department will not issue a separate permit for construction in State navigable waters. The certification will serve as the permit.” 25A S.C. Code Ann. Regs. 61-101(A)(9) (Supp. 2006).

Finally, since WPA permit application is for an activity within the State’s coastal zone, review by the Department’s Office of Ocean and Coastal Resource Management, described as a coastal zone consistency certification, is required under 15 CFR 930.57:

Following the appropriate coordination and cooperation with the State agency, all applicants for required federal licenses or permits subject to State agency review shall provide in the application to the federal licensing or permitting agency a certification that the proposed activity complies with and will be conducted in a manner consistent with the management program.

15 CFR 930.64 provides that [f]ollowing receipt of a State agency objection to a consistency certification, the Federal agency shall not issue the federal license or permit except as provided in subpart H of this part.”

The Department’s procedures allow for combined coastal zone consistency review and 401 water quality certification review as set forth in 25A S.C. Code Reg. 61-101(A)(7):

For Federal permits that require both a water quality certification and a coastal zone consistency certification, the coastal zone consistency certification determination shall be issued as a component of, and concurrently with, the water quality certification ….

Permit Certifications

The Department’s 401 Water Quality Certification and Coastal Zone Consistency were triggered by the permit applicant’s request for a permit from the U. S. Army Corps of Engineers in accordance with the Clean Water Act, 33 U.S.C. §1344. Petitioners maintain that the issuance of a 401 Water Quality Certification, Navigable Waters Permit, and Coastal Zone Consistency Certification were wrongfully made.

Coastal Management Certification

Pursuant to 25A S.C. Code Ann. Reg. 61-101 and the policies set forth in the S.C. Coastal Zone Management Program Document, WPA is required to demonstrate that there are no feasible alternatives to its proposal to dispose of dredged material in the 12.8 acre spoil disposal area. The Coastal Management Program also provides that any residential project which “requires filling or other permanent alteration of salt, brackish or freshwater wetlands will be denied, unless no feasible alternatives exist or an overriding public interest can be demonstrated.” Coastal Management Program policy Chapter III, Policy Section I(1)(b) & (e). This policy applies to wetlands, whether or not they are isolated from surrounding waters by a dike or whether they are open to tidal flow via breaches in a dike.

“Feasible alternative” is undefined in Regulation 61-101. “Where a word is not defined in a statute, our appellate courts have looked to the usual dictionary meaning to supply its meaning.” Lee v. Thermal Engineering Corp., 352 S.C. 81, 91-92, 572 S.E.2d 298, 303 (Ct. App. 2002); see also State v. Landis, 362 S.C. 97, 606 S.E.2d 503 (Ct. App. 2004) (“When faced with an undefined statutory term, the court must interpret the term in accord with its usual and customary meaning.”). “Feasible” is defined in the dictionary as “capable of being done or carried out” and “reasonable, likely.” Merriam-Webster’s Online Dictionary, http://www.merriam-webster.com/dictionary.

This dictionary meaning accords with the definition contained in the regulations governing permits for construction in navigable waters, 23 S.C. Code Ann. Regs. 19-450.2(G).[12] There, the definition of feasible includes “the concepts of reasonableness and likelihood of success of achieving the purpose.” Moreover, Regulation 19-450.2(G) further provides that the Department is authorized to consider “economic” and “social” factors when determining the feasibility of a particular alternative. Likewise, Regulation 61-101(F)(5), in requiring that a certification be denied when there is a feasible alternative, does so under the caveat that the alternative “reduces adverse consequences on water quality and classified uses.” That caveat also recognizes that the alternative must have a reasonable purpose. Therefore, not only must a “feasible alternative” be possible, but it must also be reasonable. Furthermore, in making the analysis of reasonableness, it is proper to weigh the economic cost of the proposed alternatives.

Petitioners identified one alternative – that of using a community dock and boat ramp.[13] Respondent WPA also identified the dewatering and geotextile tube alternatives. None of those alternates are reasonable under the circumstances of this case. The proposal to allow the canals to silt in and become non-functioning is, in its purest sense, an alterative to activity, but it is manifestly not a reasonable one. This alternative would eliminate navigation in established waterways and would result in loss of important ecological functions and values in the canals. It also is not a viable alternative to replace the significant number of docks that have access to the canals themselves and the waterways of the surrounding area. Thus, this alternative is not only infeasible, but such an alternative would be adverse to the overriding public interest.

The dewatering and geotextile tube alternatives are also not feasible. Though these alternatives would allow dredging of the canals, the significant cost of those methods of spoil disposal is economically prohibitive. Moreover, that cost is further magnified by the environmental impact (though much less than the proposed project) upon the upland disposal elsewhere. Accordingly, based upon the above facts, the dewatering and geotextile tube alternatives are also not feasible alternatives.

401 Water Quality Certification

The criteria for the 401 Water Quality Certification are found primarily at 25A S.C. Code Ann. Reg. 61-101. The relevant provisions for a Navigable Waters Permit are found at 23 S.C. Code Ann. Regs. 19-450. In assessing the water quality impacts of a project, the following factors should be considered:

(a) whether the activity is water dependent and the intended use of the activity;

(b) whether there are feasible alternatives to the activity;

(c) all potential water quality impacts of the project, both direct and indirect, over the life of the project . . .

25A S.C. Code Ann. Reg. 61-101(F)(3). Regulation 61-101(F)(5) further sets forth the standards when the Department must deny water quality certification. Petitioners contend that Regulation 61-101(F)(5) (a) and (b) require that this certification be denied. Those provisions state that the certification must be denied if:

(a) the proposed activity permanently alters the aquatic ecosystem in the vicinity of the project such that its functions and values are eliminated or impaired;

(b) there is a feasible alternative to the activity, which reduces adverse consequences on water quality and classified uses.

25A S. C. Code Ann. Reg. 61-101(F)(5) (a) and (b).

Here, the environmental impact is limited to the existing 12.8 acre area spoil disposal site. That site does not, as the Petitioners contend, constitute the entire “aquatic ecosystem in the vicinity of the project.” As noted above, the vicinity of the project is rather the canals in Wedgefield Plantation, the marshes surrounding the Black River, and the Black River. Since the spoil disposal area is separated from the Black River and the surrounding marshes, it will not impact or permanently alter that adjacent aquatic ecosystem. Therefore, the evidence did not establish that the removal of the functions and values of the wetlands within the spoil disposal area will have an adverse impact on water quality in the adjacent aquatic ecosystem. Moreover, as explained above, there are no other feasible alternatives to the proposed project which reduces adverse consequences on water quality and classified uses.

Res Judicata

Petitioners argue that the doctrine of res judicata barred WPA from reapplying for 401 water quality certification and coastal zone consistency certification after the Department denied WPA’s 2003 application on July 28, 2004. Petitioners contend that, because the Department’s 2004 denial decision was not appealed, it must be given preclusive effect. The Court disagrees.

Res judicata is a court-created rule that “is designed to draw a line between the meritorious claim on the one hand and the vexatious, repetitious and needless claim on the other hand.” Purter v. Heckler, 771 F.2d 682, 689-90 (3rd Cir. 1985). Generally speaking, it bars subsequent actions “by the same parties on the same issues,” as well as subsequent actions by the same parties when the claims arise out of the same transaction or occurrence that was the subject of a prior action between those parties. Sub-Zero Freezer Co. v. R.J. Clarkson Co., 308 S.C. 188, 190-91, 417 S.E.2d 569, 571 (1992). Under the doctrine of res judicata, “[a] litigant is barred from raising any issues which were adjudicated in the former suit and any issues which might have been raised in the former suit.” Hilton Head Center of South Carolina, Inc. v. Pub. Serv. Comm’n of South Carolina, 294 S.C. 9, 11, 362 S.E.2d 176, 177 (1987).

Res judicata is based on the judicial policy that “a losing litigant deserves no rematch after a defeat fairly suffered, in adversarial proceedings, on an issue identical in substance to the one he subsequently seeks to raise.” Astoria Federal Savings & Loan Ass’n v. Solimino, 501 U.S. 104, 107 (1991). A contrary rule “would, as a general matter, impose unjustifiably upon those who have already shouldered their burdens, and drain the resources of an adjudicatory system with disputes resisting resolution.” Id. at 107-08. Nevertheless, “[b]ecause res judicata may govern grounds and defenses not previously litigated” thereby “blockad[ing] unexplored paths that may lead to truth,” it should be invoked “only after careful inquiry.” Brown v. Felsen, 442 U.S. 127, 132 (1979). “The ease and efficiency of res judicata as a means of quickly avoiding an evaluation of the merits of a plaintiff’s claim does not imply that the decision to apply the doctrine should be either facile or hasty.” Purter v. Heckler, 771 F.2d at 690.

The doctrine of res judicata may, under certain circumstances, apply to decisions of administrative agencies. In Astoria, the U.S. Supreme Court explained that “[w]hen an administrative agency is acting in a judicial capacity and resolves disputed issues of fact properly before it which the parties have had an adequate opportunity to litigate, the courts have not hesitated to apply res judicata to enforce repose.” Astoria, 501 U.S. at 107 (quoting United States v. Utah Constr. & Mining Co., 384 U.S. 394, 422 (1966)). However, the court cautioned that “[a]lthough administrative estoppel is favored as a matter of general policy, its suitability may vary according to the specific context of the rights at stake, the power of the agency, and the relative adequacy of agency procedures.” Astoria, 501 U.S. at 109-10. Courts, in interpreting Astoria, have held that an agency acts in a “judicial capacity” when it provides the following safeguards: (1) representation by counsel, (2) pretrial discovery, (3) the opportunity to present memoranda of law, (4) examinations and cross-examinations at the hearing, (5) the opportunity to introduce exhibits, (6) the chance to object to evidence at the hearing, and (7) final findings of fact and conclusions of law. Reed v. AMAX Coal Co., 971 F.2d 1295, 1300 (7th Cir. 1992) (per curiam); In re Kaiser Aluminum Corp., 365 B.R. 447 (D. Del. 2007); Durko v. OI-NEG TV Products, 870 F. Supp. 1278 (M.D. Pa. 1994); Buckley v. U.S., 51 Fed. Cl. 174 (Fed. Cl. 2001); see also In Maryland State Dep’t of Educ. v. Shoop, 704 A.2d 499 (Md. Ct. App. 1998) (in holding that the Maryland State Department of Education was not acting in a “judicial capacity” when it suspended a vocational instructor for violating tool security policies, Maryland Court of Appeals explained that the hearing was not conducted by a judicial officer, the proceedings were not recorded in any way, and no rules of evidence or trial procedure were recognized); Delamater v. Schweiker, 721 F.2d 50, 53 (2d Cir. 1983) (per curiam) (“An action taken by an administrative agency to grant or deny a benefit is not an adjudicated action unless the agency has made its decision using procedures substantially similar to those employed by the courts.”).

In this case, Petitioners have not contended that the safeguards described above were present during the application process that ultimately led to DHEC staff’s denial of WPA’s 2003 application. Moreover, it is notable that, as discussed above, at the time of the denial of WPA’s 2003 application, DHEC staff decisions were reviewed by the ALC as “contested cases” and thus de novo. S.C. Code Ann. § 1-23-610 (2005); Marlboro, 358 S.C. at 579, 595 S.E.2d at 854 (ALJs hear contested cases de novo).[14] This fact suggests that the General Assembly did not view the decision process utilized by DHEC staff as containing the types of safeguards that would warrant the application of res judicata to its unappealed decisions. Accordingly, the Court concludes that the doctrine of res judicata did not bar Respondent from reapplying for 401 water quality certification and coastal zone consistency certification.

The two primary cases relied upon by Petitioners, Leviner v. Richardson, 443 F.2d 1338 (4th Cir. 1971) and S.C. Dep’t of Social Servs. v. Winyah Nursing Homes, Inc., 282 S.C. 556, 320 S.E.2d 464 (Ct. App. 1984), do not mandate a different result. In Leviner, the plaintiff filed an application seeking disability benefits. His application was denied, without a hearing, on the basis that his disability was not present at the time his insured status had expired. The plaintiff did not request reconsideration of the denial decision, but subsequently filed a second, third and fourth application for benefits. All of his ensuing applications were denied. On appeal of the denial of the plaintiff’s fourth application, the Fourth Circuit held that the doctrine of res judicata “may apply” in cases where no administrative hearing was requested or held. Leviner, 443 F.2d at 1343. However, the court also noted that:

In Grose v. Cohen, supra, we said that the doctrine [of res judicata], as applied to administrative decisions, “is not encrusted with the rigid finality that characterizes the precept in judicial proceedings.” We added that “practical reasons may exist for refusing to apply it” and “when traditional concepts of res judicata do not work well, they should be relaxed or qualified to prevent injustice.”

Id. at 1342 (quoting Grose v. Cohen, 406 F.2d 823, 824-825 (4th Cir. 1969) (internal citations omitted). The court further held that a prior administrative determination should not be res judicata “where new and material evidence is offered which is of sufficient weight that it may result in a different determination.” Id. at 1343. Ultimately, the court chose to remand the case to the district court for it to decide whether the evidence proffered in support of the plaintiff’s fourth application could be deemed “new and material evidence” sufficient to result in a different determination. Id.

Leviner, a Fourth Circuit case, is not binding on this Court. However, even it were binding, the Court concludes that “practical reasons” exist for refusing to apply administrative res judicata in this case. First, the Department has admitted that its denial of WPA’s 2003 permit was largely based upon its erroneous assumption that the embankment surrounding the spoil disposal area had been breached. This admission is significant since courts have refused to apply administrative res judicata in cases where there is manifest error in the record. See, e.g., Oubre v. District of Columbia Dep’t of Employment Servs., 630 A.2d 699 (D.C. 1993); Grose v. Cohen, 406 F.2d 823 (4th Cir. 1969); Purter, 771 F.2d 682; Perkins v. Kramer, 198 P.2d 475 (Mont. 1948); see also Wright v. Marlboro County School Dist., 317 S.C. 160, 452 S.E.2d 12 (Ct. App. 1994) (res judicata does not apply in cases where an administrative tribunal is asked to judge allegations of its own wrongdoing). Similar to those cases, the Department’s admission that its denial of WPA’s 2003 application was based primarily on its misunderstanding of a material fact relating to the condition of the proposed disposal site cautions against a rigid application of res judicata in this case.

Second, WPA’s 2006 application is different than WPA’s 2003 application. As discussed above, the 2006 application differs from the 2003 application in that the size of the “existing confined disposal basin” is now shown as 12.8 acres, the depth of dredging has been adjusted in one section of the canals, the width of the dredge cut has been reduced to allow for a 10’ wide buffer on either side of the canal, and the shape of the dredge cut has been altered from a box cut to a “v” shaped cut. The Department apparently viewed these changes (along with its reversal in opinion regarding the existence of a breach in the spoil disposal basin) as sufficient to result in a “different determination” ― as discussed, the Department approved the 2006 application whereas it had denied the 2003 application. Thus, these changes to WPA’s application constitute another “practical reason” for refusing to apply res judicata here.

Like Leviner, Winayh also does not mandate the application of res judicata in this case. In Winayh, the Department of Social Services (DSS) brought an action against a corporate nursing home and several of its officers, directors and shareholders to enforce a final agency decision that found the nursing home liable for medicaid overpayments. The final agency decision sought to be enforced by DSS had been made by DSS after a “fair hearing,” and it had not been appealed by the nursing home. In the action to enforce the final agency decision, the nursing home’s principal shareholder sought to raise issues that could have been, but were not, raised at the fair hearing. On appeal of the matter, the Court of Appeals held that the doctrine of res judicata precluded the raising of those issues, concluding that “the unappealed DSS decision bound the Nursing Home and its privies on all issues that were or could have been addressed at the fair hearing.” Winyah, 282 S.C. at 563, 320 S.E.2d at 468.

In this case, Petitioners have not contended that anything resembling a “fair hearing” was held when Respondent’s 2003 application was denied in 2004.[15] Accordingly, Winyah does not dictate the application of res judicata here.

Timeliness

Respondent WPA argues that the ALC does not have jurisdiction over this matter because Petitioners failed to comply with the statutory procedural prerequisites for perfecting contested case review of the Department’s decision. S.C. Code Ann § 44-1-60(E) provides that:

Notice of the department decision must be sent to the applicant, permittee, licensee, and affected persons who have asked to be notified by certified mail, return receipt requested. The department decision becomes the final agency decision fifteen days after notice of the department decision has been mailed to the applicant, unless a written request for final review is filed with the department by the applicant, permittee, licensee, or affected person.

(emphasis added). Therefore, Section 44-1-60(E) sets forth a fixed period of time by which an affected person can seek review of a Final Department Determination. Moreover, if a party fails to meet the deadline for requesting a review before the Department’s Board, the decision becomes the final agency decision. At that point, the DHEC Board lacks jurisdiction to “validly exercise dominion over the matter” and the ALC thus cannot subsequently invoke jurisdiction to hear the matter. South Carolina Coastal Conservation League v. South Carolina Dept. of Health and Environmental Control, South Carolina Department of Transportation, and South Carolina State Ports Authority, --- S.E.2d ----, 2008 WL 4693075 (Ct. App. 2008).

The Department clearly issued its 401 water quality certification on July 13, 2007. However, Section 44-1-60(E) requires that a request for a Final Review Conference be filed within fifteen days of mailing of notice of the department decision, not fifteen days from the issuance of the decision. Here, the evidence simply did not establish when the Notice of the Department’s decisions was mailed. Accordingly, since there is no date to show when the mandatory fifteen day deadline began running, Respondent failed to establish that the request for a Final Review Conference was untimely.

Moreover, even if the Court presumes that the Notice was mailed on the date that it was issued, the fifteenth day after July 13, 2007 was July 28, 2007, a Saturday. Generally, “if the last day for the performance of an act falls on a Saturday, Sunday or holiday the period will be extended and the act may be performed on the following secular or business day.” C.J.S. Time § 42 (2006). This tenet is specifically applicable to the filing of request for judicial proceedings. See C.J.S. Time § 43 (2006) (“If the last day of a period allowed by law for taking any stated action in a judicial proceeding falls on a Saturday, Sunday, or legal holiday, the general rule is to exclude such terminal Saturday, Sunday, or holiday, and to allow the action to be taken the following day.”). South Carolina has followed this rule for computing timeframes to take action in the South Carolina Rules of Civil Procedure. SCRCP Rule 6, which mirrors SCALC Rule 3, states that:

In computing any period of time prescribed or allowed by these rules, by order of court, or by any applicable statute, the day of the act, event, or default after which the designated period of time begins to run is not to be included. The last day of the period so computed is to be included, unless it is a Saturday, Sunday or a State or Federal holiday, in which event the period runs until the end of the next day which is neither a Saturday, Sunday nor such holiday.

Likewise, in the administrative venue, ALC Rule 3(A) provides that:

In computing any period of time prescribed or allowed by these rules, by order of court, or by any applicable statute, the day of the act, event, or default after the designated period of time begins to run is not included. The last day of the period so computed is to be included, unless it is a Saturday, Sunday or a State or Federal holiday, in which event the period runs until the end of the next day which is neither a Saturday, Sunday nor such holiday.

In fact, the Department itself has taken this position. When issuing its notice of proposed decision, the Department attaches a “Notice of Appeal Procedure” which specifically states that:

In order to be timely, a request for final review must be received by the Clerk of the Board within 15 days after notice of the decision has been mailed to the applicant or respondent. If the 15th day occurs on a weekend or State holiday, the request is due to be received by the Clerk of the Board on the next working day.

Therefore, the result that WPA proposes would ignore an overwhelming body of law that would allow Petitioners to file on a Monday when the statutory deadline terminated on a Saturday, and would ignore the Department’s own application of the statute. I find Petitioner’s interpretation to be clearly erroneous. Furthermore, the Department is a State office that is not open for business on Saturday or Sunday. The Clerk of the Board would thus not be present to clock in a request for review conference on a Saturday or Sunday. Consequently, under WPA’s reasoning, the last day for filing a request for review would be on a day in which such a request could not be filed, thereby reducing the limited timeframe to fourteen days. I find that such reasoning would lead to an absurd result. See Kiriakides v. United Artists Communications, Inc., 312 S.C. 271, 275, 440 S.E.2d 364, 366 (1994) (when construing a statute, the Court will reject meaning that would lead to an absurd result not intended by the legislature).

In this case, the next day which is not a Saturday or a Sunday was Monday, July 30, 2007 – the date that Petitioners filed their request for a Final Review Conference with the Clerk of the DHEC Board. Thus, I find that Petitioners’ request was filed within the statutory fifteen-day time period prescribed in Section 44-1-60(E).

ORDER

IT IS HEREBY ORDERED that the Department shall issue to WPA the Water Quality Certification and Coastal Zone Consistency Certification requested by WPA pursuant to its permit application filed on May 31, 2006 and subsequently revised on November 2, 2006.

AND IT IS SO ORDERED.

_________________________________

Ralph King Anderson III

Administrative Law Judge

December 15, 2008

Columbia, South Carolina



[1] Petitioners also argued that contact made to the Department’s staff on behalf of WPA by two state Senators improperly influenced the Department’s decision regarding this issue. I find that the contact only encouraged the Department to objectively review this matter and had no impact regarding the Department’s ultimate decision. Moreover, “[a]n adequate de novo review renders harmless a procedural due process violation based on the insufficiency of the lower administrative body.” Unisys Corp. v. S.C. Budget and Control Bd. Div. of General Services Info. Tech. Mgmt. Office, 346 S.C. 158, 174, 551 S.E.2d 263, 272 (2001). The ALC, as part of the executive branch of South Carolina government, provides an adequate de novo review of this matter, thereby rendering any potential due process violation by the Department harmless.

[2] Between the issuance of the1970 permit and the 1982 application, the federal Clean Water Act and the South Carolina Coastal Zone Management Act (SCCZMA) were passed into law. The Clean Water Act required a Section 404 permit to discharge dredged or fill material into waters of the United States, which included placing dredged spoil material in wetlands. 33 U.S.C. §1344. Along with the new 404 Clean Water Act permit, the State also had to issue a 401 water quality certification, pursuant to Section 401 of the Clean Water Act, and a coastal zone consistency certification, pursuant to the SCCZMA. 33 U.S.C. §1341; S.C. Code Ann. §48-39-80.

[3] Prior to the passage of 2006 S.C. Act No. 387 (effective July 1, 2006), DHEC staff determinations were reviewed by the ALC pursuant to a contested case proceeding, and decisions of the ALC were then reviewed on appeal by the DHEC Board. See S.C. Code Ann. §§ 1-23-600 & 1-23-610 (2005). Currently, those aggrieved by a DHEC staff decision must first seek review by the DHEC Board before requesting a contested case proceeding with the ALC. See S.C. Code Ann. § 44-1-60 (Supp. 2007).

[4] Maintenance dredging occurred following issuance of the 1983 permit, but it is unclear whether it occurred before or after entry of the Consent Order on March 25, 1986.

[5] The nomenclature used to identify the proposed spoil disposal area has been, to say the least, varied. WPA referred to the area in its permit application as an “existing disposal basin,” and it is depicted as a “proposed confined disposal basin.” The Corps of Engineers, in its March 9, 2007, Public Notice, described the spoil disposal area as a “disposal basin.” OCRM staff described it as a “spoil site” in the coastal zone consistency certification and Bureau of Water staff described it as a “confined disposal facility” in its certification. The DHEC Board referred to it as “an existing confined disposal facility” in its Final Agency Decision. I find that the terms “contained disposal facility” and “confined disposal facility” are synonymous and used interchangeably to describe the disposal area.

The term “contained disposal facilities” is used within 33 U.S.C. §1293(a), the Federal Water Pollution Control Act. In accordance with 33 U.S.C. §1293(a), the Secretary of the Army, acting through the Chief of Engineers, is authorized to “construct, operate, and maintain … contained disposal facilities.” Robert H. Riggs, who was employed by the Charleston District Corps of Engineers for 37 years and was qualified by the court as an expert in the federal regulatory process, described the spoil disposal area as a “confined disposal facility.” According to Mr. Riggs, the Corps commonly referred to disposal facilities like the one utilized by WPA as “confined disposal facilities.” Jeff Thompson, the Department’s wetland biologist who reviewed the permit application, also referred to the spoil disposal area as a “contained disposal facility” and testified that the term was commonly used by regulatory agencies.

[6] There is a difference in the size of the spoil disposal area between what was authorized in the 1983 permit (9.2 acres) and what exists today (12.8 acres). However, the Corps follows regulatory guidance that requires the Corps to proceed with enforcement within five years of the discovery of a compliance issue if it wishes to pursue enforcement of an issue. Here, the Corps has had since the mid-1980’s to consider an enforcement action to remediate the established size of the spoil basin. Accordingly, I find that the existing disposal area is 12.8 acres.

[7] The flashboard riser functions to release water at set elevations and to prevent water from flowing back onto the site. Likewise, the overflow pipe is set at a high elevation in the embankment and its purpose is to allow water out at higher elevations in rainfall or flooding events to prevent breach or loss of the embankment.

[8] There is dispute between the parties as to the condition of the acreage ultimately approved in 1983 for spoil disposal. Petitioners argue that the original spoil disposal basin was constructed out of uplands. However, the evidence established that the spoil disposal area was an intact isolated rice field, called an upland, because it was above high water. As explained by both WPA’s expert and OCRM’s wetland biologist, even if the area was described as an upland disposal site in 1983, the basis for that description was simply that it was above mean high water. In fact, the South Carolina Wildlife and Marine Resources Department commented in the 1983 permit application that: “The proposed spoil area, although diked at one time is presently a vegetated wetland over 75 percent of the area …”

[9] WPA’s only funding mechanism for the dredging project is through assessments of its property owners.

[10] Though the geotextile tubes alterative also allowed for WPA to just leave the tubes in place as bulkheading along the canals, this alternative was not feasible because of the narrow width of the canals.

[11] In accordance with 33 U.S.C. § 1344 (d), “Secretary … means the Secretary of the Army, acting through the Chief of Engineers.”

[12] DHEC is required to consider permits for construction in navigable waters in the context of this water quality certification review. See Regs. 61-101(A)(9) (water quality certification review for activities requiring both water quality certification and a permit for construction in navigable waters will encompass issues pertaining to the navigable waters permit as well). Thus, the definitions governing navigable waters permits are instructive in this case.

[13] Petitioners also argued that neither WPA nor the Department presented any evidence about why other alternatives are not feasible. In that regard, the Court notes that the Petitioners bore the burden of proof in this case. See Leventis, 530 S.E.2d 643.

[14] “A trial de novo is one in which ‘the whole case is tried as if no trial whatsoever had been had in the first instance.’” Marlboro, 358 S.C. at 579, 595 S.E.2d at 854 (quoting Blizzard v. Miller, 306 S.C. 373, 375, 412 S.E.2d 406, 407 (1991)).

[15] At the time of the Winayh decision, the procedures for DSS “fair hearings” were set forth in 27 S.C. Code Regs. 114-110 (1976). Regulation 114-110 granted litigants trial-type safeguards such as the right to be represented by counsel, the opportunity to present evidence and to advance arguments, and the chance to call and cross-examine witnesses. Findings of the Fair Hearing Committee of DSS were reviewed on appeal under a “substantial evidence” standard. See, e.g., Babcock Center, Inc. v. Office of Audits, 286 S.C. 398, 334 S.E.2d 112 (1985).


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