1. Generally: No person shall drain or fill a wetland, wholly or partially, without first having a wetland value replacement plan approved by the City Council consistent with this chapter and provided, that the activity is not prohibited under the special considerations provisions in subsection D9 of this section.
2. Preapplication Conference And Site Visit: Before preparation of a wetland value replacement plan, the landowner must meet with the City for a preapplication conference and site visit. A landowner may submit the sequencing information required in subsection B of this section and request a determination of compliance with the sequencing requirements from the City before preparing a replacement plan.
3. Evaluation: Technical questions concerning the public value, location, size, and type of wetland shall be submitted to the technical evaluation panel. Wetland boundaries must be determined using the methodologies in the Federal Manual for Identifying and Delineating Jurisdictional Wetlands (January 1989).
Wetland type must be identified according to Cowardin, et al., 1979, Classification of Wetlands and Deepwater Habitats of the United States and according to United States Fish and Wildlife Service Circular No. 39 (1971 edition) "Wetlands of the United States". The technical evaluation panel will provide its determinations to the City for consideration.
1. Requirement: Except for wetlands located in cultivated fields that are subject to subsection B8 of this section, and calcareous fens that are subject to subsection B9 of this section, the City will not consider or approve a wetland replacement plan unless the City finds that the applicant has demonstrated that the activity impacting a wetland has complied with all of the following principles in descending order or priority:
a. Avoids direct or indirect impacts to the wetland that may destroy or diminish the wetland under the criteria in subsection B3 of this section;
b. Minimizes the impact to the wetland by limiting the degree or magnitude of the wetland activity and its implementation under the criteria in subsection B4 of this section;
c. Rectifies the impact by repairing, rehabilitating, or restoring the affected wetland under the criteria in subsection B5 of this section;
d. Reduces or eliminates the impact to the wetland over time by preservation and maintenance operations under the criteria in subsection B6 of this section; and
e. Replaces unavoidable impacts to the wetland by restoring or creating substitute wetland areas having equal or greater public value as provided in this chapter.
2. Application Options: An applicant may either submit the information required for sequencing analysis as part of the application for replacement plan approval or apply for a preliminary sequencing determination from the City before preparing a replacement plan. The City may request additional information needed to make a determination. For projects impacting wetland areas less than 0.1 acre, the City may provide an on site sequencing determination without written documentation from the applicant.
3. Determination Of Impact Avoidance:
a. Avoidance Required: Avoidance will be required when indicated by special considerations as stated in this chapter.
b. Wetland Dependence Determination:
(1) Based on information provided by the applicant, the City will determine if the proposed project is wetland dependent. A project is wetland dependent if wetland features, functions, or values are essential to fulfill the basic purpose of the project. A wetland present at the site of a proposed project does not make that project wetland dependent.
(2) A project that has been determined by the City to be wetland dependent is exempt from the analysis of avoidance alternatives in subsection B3c of this section.
(1) The applicant shall provide the City with documentation describing at least two (2) alternatives in addition to the proposed project, one of which may be the no-build alternative, that would avoid impacts to wetlands. The alternatives may include consideration of alternate sites or alternative project configurations on the proposed site. The alternatives must be judged by the City as good faith efforts, or the City will require the applicant to redraft them for reconsideration.
(2) The City will determine whether any feasible and prudent alternatives are available that would avoid impacts to wetlands. An alternative will be considered feasible and prudent if it is capable of being done from an engineering point of view, is in accordance with accepted engineering standards and practices, is consistent with reasonable requirements of the public health, safety, and welfare, is an environmentally preferable alternative based on a review of social, economic, and environmental impacts, and would create no truly unusual problems. The City will consider the following in evaluating alternatives as applicable:
(A) Whether the basic project purpose can be reasonably accomplished using one or more other sites in the same general area that would avoid wetland impacts. An alternate site will not be excluded from consideration only because it includes or requires an area not owned by the applicant that could reasonably be obtained, used, expanded, or managed to fulfill the basic purpose of the proposed project;
(B) The general suitability of alternate sites considered by the applicant;
(C) Whether reasonable modification of the size, scope configuration, or density of the project would avoid impacts to wetlands;
(D) Efforts by the applicant to accommodate or remove constraints on alternatives imposed by zoning standards or infrastructure, including request for conditional use permits, variances, or planned unit developments; and
(E) The physical, economic and demographic requirements of the project. Economic considerations alone do not make an alternative not feasible and prudent.
(3) If the City determines that a feasible and prudent alternative exists that would avoid impacts to wetlands, it will deny the replacement plan. If no feasible and prudent alternative is available that would avoid impacts to wetlands, the City will evaluate the replacement plan for compliance with subsections B4 to B6 of this section.
4. Determination Of Impact Minimization:
a. The applicant shall demonstrate to the City satisfaction that the activity will minimize impacts to wetlands. In reviewing the sufficiency of the applicant's efforts to minimize wetland impacts, the City will consider:
(1) The spatial requirements of the project;
(2) The location of existing structural or natural features that may dictate the placement or configuration of the project;
(3) The purpose of the project and how the purpose relates to placement, configuration, or density;
(4) The sensitivity of the site design to the natural features of the site, including topography, hydrology and existing vegetation;
(5) The value, function, and spatial distribution of the wetlands on the site;
(6) Individual and cumulative impacts; and
(7) An applicant's efforts to:
(A) Modify the size, scope, configuration, or density of the project;
(B) Remove or accommodate site constraints including zoning, infrastructure, access, or natural features; and
(C) Otherwise minimize impacts.
b. If the City finds that an applicant has not complied with the requirements to minimize wetland impacts, the City will list, in writing, its objections to the project. If, within thirty (30) days, the applicant does not withdraw the project proposal or indicate intent to submit an amended project proposal satisfying the City's objections, the statement of objections shall constitute a denial.
5. Determination Of Impact Rectification: Temporary impacts to a wetland must be rectified by repairing, rehabilitating, or restoring the affected wetland.
a. Activities may qualify for a no-loss determination in section
11-93-7 of this chapter by meeting all of the following conditions:
(1) The physical characteristics of the affected wetland, including ground elevations, contours, inlet dimensions, outlet dimensions, substrate, and hydrologic regime, are restored to preproject conditions sufficient to ensure that all preproject functions and values are restored;
(2) The activity is completed and the physical characteristics of the wetland are restored within six (6) months of the start of the activity; and
(3) The party responsible for the activity provides a performance bond to the City for an amount sufficient to cover the estimated cost to restore the wetland to preproject conditions. The City will return the performance bond to the responsible party upon a determination by the City that the conditions in this subsection and subsection B5b of this section have been met.
b. An applicant shall be granted a no-loss determination under the criteria in subsection B5a of this section once in a ten (10) year period for a particular site within a wetland; except, that repairs to the original project shall be allowed under the no- loss determination, if the City determines the request to be necessary and reasonable.
c. Wetland impacts that do not qualify for a no-loss determination according to the criteria in subsection B5a of this section are subject to replacement under the criteria in subsections C to I of this section.
6. Determination Of Reduction Of Elimination Of Impacts Over Time: After an activity is completed, further wetland impacts from the draining or filling must be reduced or eliminated by maintaining, operating, and managing the project in a manner that preserves and maintains remaining wetland functions and values. The City will require applicants to implement Best Management Practices to protect wetland functions and values.
7. Unavoidable Impacts: Unavoidable wetland impacts that remain after efforts to minimize, rectify, or reduce or eliminate them must be replaced according to subsections B to I of this section.
8. Wetlands On Cultivated Fields: If the wetland is located on a cultivated field, replacement must be accomplished through restoration without regard to the priority order in subsection B1 of this section. A wetland drained or filled under this provision must not be converted to nonagricultural land for ten (10) years. The landowner must execute and record a notice of this requirement in the Office of the County Recorder for Wright County.
9. Calcareous Fens: Calcareous fens, as identified by the Commissioner, may not be filled, drained, or otherwise degraded, wholly or partially, by any action, unless the Commissioner, under an approved management plan, decides some alteration is necessary, as provided in this chapter. (Prior Code § 20-93-14)
C. Replacement Plan Components: On an application form provided by the City and with needed attachments supplied by the applicant, the following documentation must be provided, except that, for replacement plans utilizing the wetland bank as provided by section
11-93-15 of this chapter. Subsections C2 and C4 of this section do not apply; instead the applicant shall submit the credit transfer form. (Prior Code § 20-93-14; amd. 2018 Code)
1. Organizational information, including the following:
a. The Post Office address of the applicant;
b. For corporations, the principal officers of the corporation, any parent companies, owners, partners, and joint venturers, and a designated contact person;
c. Managing agents, subsidiaries, or consultants that are or may be involved with the wetland draining or filling project;
2. Either an affidavit confirming that the wetland values will be replaced before or concurrent with the actual draining or filling of a wetland or an irrevocable bank letter of credit to guarantee the successful completion of the wetland value replacement;
3. For the impacted wetland:
a. A recent aerial photograph or accurate map of the impacted wetland area;
b. The location of the wetland, including the County, watershed name or number, and public land survey coordinate of approximate wetland center;
c. The size of the wetland, in acres or square feet;
d. The type of wetland using United States Fish and Wildlife Service Circular No. 39 (1971 edition) and National Wetland Inventory mapping conventions (Cowardin et al., 1979);
e. A list of the dominant vegetation in the impacted wetland area, including common names of the vegetation exceeding twenty percent (20%) coverage and an estimate of coverage, for example, fifty percent (50%) willow, twenty percent (20%) cattails, and thirty percent (30%) sedge;
f. A soils map of the site showing soil type and substrate, where available;
g. The size of the watershed that drains surface water into the wetland as determined from a United States Government Survey topographical map or other suitable topographical survey;
h. The locations of any surface inlets or outlets, natural or otherwise, draining into or out of the wetlands, and if the wetland is within the floodplain of a stream, river, or other watercourse, the distance and direction to the watercourse;
i. A map, photograph, or written description of the land use of the immediate watershed within one mile of the impacted wetland. The surrounding land use information shall also indicate the presence and location, if any, of wetland preservation regions and areas, wetland development avoidance regions and areas, and wetland deficient regions and areas as identified in the comprehensive water plan;
j. The nature of the proposed project, its areal extent, and the impact on the wetland must be shown in sufficient detail to allow the City to determine the amount and types of wetland to be impacted and to demonstrate compliance with the replacement sequencing criteria in subsection B of this section if applicable;
k. Evidence of ownership or rights to the affected areas, including a legal description. When two (2) or more landowners are involved, including both the impact site and the proposed replacement site, a contract or other evidence of agreement signed by all landowners and notarized must be included with the replacement plan. The contract or agreement must contain an acknowledgement of the covenant provisions in subsection C4f of this section by landowners on which a replacement wetland is proposed and the location and acreage of replacement wetlands. The contract becomes binding upon final approval of the replacement plan;
l. A list of all other local, State, and Federal permits and approvals required for the activity; and
m. Other information considered necessary by the City for evaluation of the activity.
4. For the replacement wetland subsections C3a to C3i and C3k to C3m of this section and:
a. An explanation of the size and type of wetland that will result from successful completion of the replacement plan;
b. Scale drawings showing plan and profile views of the replacement wetland and fixed photo reference points for monitoring purposes. Photo reference points should include views of any control structures and enough additional points to adequately depict the entire project;
c. How the replacement wetland shall be constructed, for example, excavation or restoration by blocking an existing tile; the type, size, and specifications of outlet structures; elevations, relative to mean sea level or established bench mark, of key features, for example, sill, emergency overflow, and structure height; and Best Management Practices that will be implemented to prevent erosion or site degradation;
d. For created wetlands only, additional soils information sufficient to determine the capability of the site to produce and maintain wetland characteristics;
e. A timetable that clearly states how and when implementation of the replacement plan shall proceed, and when construction of the replacement wetland shall be finalized;
f. A notice in a form provided by the board attached to and recorded with the deed for lands containing a replacement wetland, specifying the following:
(1) The location of the replacement wetland; (Prior Code § 20-93-14)
(2) That the wetland is subject to the Wetland Conservation Act; (Prior Code § 20-93-14; amd. 2018 Code)
(3) That the fee title owner is responsible for the costs of repairs or reconstruction, if necessary, or for replacement costs;
(4) That reasonable access to the replacement wetland shall be granted to the proper authorities for inspection, monitoring, and enforcement purposes;
(5) That costs of title review and document recording is the responsibility of the fee title owner; and (Prior Code § 20-93-14)
(6) That the City or board can require necessary repairs or reconstruction work to return the wetland to the specifications of the approved replacement plan and require reimbursement of reasonable costs from the wetland owner, or can require replacement of the wetland according to the Wetland Conservation Act; (Prior Code § 20-93-14; amd. 2018 Code)
g. A statement that the replacement wetland was not previously restored or created under a prior approved replacement plan;
h. A statement that the replacement wetland was not drained or filled under an exemption during the previous ten (10) years;
i. A statement that the replacement wetland was not restored with financial assistance from public conservation programs;
j. A statement that the replacement wetland was not restored using private funds other than those of the landowner unless the funds are paid back with interest to the individual or organization that funded the restoration and the individual or organization notifies the City in writing that the restored wetland may be considered for replacement;
k. A plan for monitoring the success of the replacement plan in meeting the project goal of subsection D1 of this section, and as specified in this chapter; and
l. Other information considered necessary for evaluation of the project by the City.
5. The applicant must provide information known to the applicant or readily available concerning the special considerations criteria in subsection D9 of this section.
D. Replacement Plan Evaluation Criteria:
1. Sequencing: Prior to the City considering or approving a replacement plan, the applicant must have exhausted all possibilities to avoid and minimize adverse wetland impacts according to sequencing in subsection B of this section. The applicant must demonstrate to the City that the replacement plan complies with this subsection and subsection E of this section.
2. Type Of Replacement: The order of preference for the method of replacement, from most preferred to least preferred, is project specific restoration, project specific creation, then wetland banking. Modification or conversion of nondegraded wetlands from one wetland type to another, for example by impoundment of additional water, does not constitute adequate replacement.
Wetlands drained or filled under an exemption may not be restored for replacement credit for ten (10) years after draining or filling.
3. Timing Of Replacement: Replacement of wetland values must be completed before or concurrent with the actual draining or filling of a wetland, unless an irrevocable bank letter of credit is submitted to the City to guarantee successful completion of the replacement. All wetlands to be restored or created for replacement must be designated for replacement before restoration or creation. Submission to the City of the information required in subsection C of this section and subsequent approval shall be considered evidence of designation for replacement, provided the information is submitted before the actual restoration or creation.
4. Location Of Replacement Wetlands: Replacement wetlands must be located within the same watershed or County as the impacted wetlands.
5. Statewide Replacement For Public Transportation Projects: Wetlands impacted by public transportation projects may be replaced Statewide, provided they are approved by the Commissioner under an established wetland banking system or under this chapter.
6. Size Of Replacement Wetlands: Replacement wetlands must be of a size sufficient to ensure that they provide equal or greater public value than the wetland that was drained or filled. For a wetland located on nonagricultural land, the minimum size of the replacement wetland must be in the ratio of two (2) acres of replaced wetland for each acre of drained or filled wetland. For a wetland located on agricultural land, the minimum size of the replacement wetland must be in the ratio of one acre of replaced wetland for each acre of drained or filled wetland. The actual replacement ratios required for a replacement wetland may be more than the minimum, subject to the evaluation of wetland functions and values. A review by the City will determine the actual required replacement ratios. Future owners may make no use of the wetland after it is altered, other than as agricultural land for a period of ten (10) years unless future replacement to achieve a two to one (2:1) ratio occurs. The landowner shall record a notice of this restriction in the Office of the Wright County Recorder.
7. Carbon Balance: When it is necessary to replace a drained or filled peat land, the replacement wetland must be revegetated with planted or naturally invading vegetation established within three (3) growing seasons.
8. Ecological Consistency: Restoration and replacement of wetlands must be accomplished according to the ecology of the landscape area affected. A replacement plan that would result in wetlands or wetland characteristics that do not naturally occur in the landscape area in which the replacement will occur will not be approved.
9. Special Considerations: The factors in subsections D9a to D9i of this section, when identified as being applicable to an impact site or a replacement site, will be considered by the City in the review of replacement plans.
a. Federal Or State Listed Endangered Species: A replacement plan for activities that involve sites where Federal or State listed endangered species are known to be present will not be approved if it is determined that the proposed activities will constitute a taking of those listed species under Minnesota Statutes section 84.0895. Limited information on the presence of listed species at a particular site is available from the department's natural heritage program. Activities that involve taking listed species are subject to Minnesota Statutes section 84.0895.
b. Rare Natural Communities: A replacement plan for activities that involve the modification of a rare natural community as determined by the department's Natural Heritage Program will not be approved if the City determines that the proposed activities will permanently adversely affect the natural community.
c. Special Fish And Wildlife Resources: A replacement plan for activities that would have a significant adverse impact that cannot be mitigated on a special or locally significant fish and wildlife resource will not be approved. These activities include, but are not limited to:
(1) Fish passage and spawning areas;
(2) Colonial water bird nesting colonies;
(3) Migratory waterfowl concentration areas;
(4) Deer wintering areas; and/or
(5) Wildlife travel corridors.
Activities involving streams must not block fish passage unless approved by the department.
d. Archaeological Or Historic Sites: A replacement plan for activities that involve the modification of known archaeological or historical sites on or eligible for the National Register of Historic Places, as designated by the State Historic Preservation Officer, will not be approved if the City determines that the proposed activities will have a significant adverse impact on the archaeological or historical value of the site.
e. Groundwater Sensitivity: A replacement plan for activities will not be approved if the City determines the activities would have a significant adverse impact on groundwater quality. The publication "Criteria and Guidelines for Assessing Geologic Sensitivity of Ground Water Resources in Minnesota" (MDNR, 1991) may be used as a guide in determining potential impacts.
f. Sensitive Surface Waters: A replacement plan will not be approved if the City determines the activities will have a significant adverse impact on the water quality of outstanding resource value waters or on trout waters designated by the Commissioner.
g. Education Or Research Use: Wetlands known to be used for educational or research purposes must be maintained or adequately replaced.
h. Waste Disposal Sites: The City will evaluate the type and amount of waste material found at the site. Activities involving known or potential hazardous wastes or contaminants must be conducted according to applicable Federal and State standards.
i. Consistency With Other Plans: The City will consider the extent to which proposed activities are consistent with other plans, such as watershed management plans, Land Use Plans, zoning, and Master Plans.
10. Evaluation Of Wetland Functions And Values: Replacement wetlands must replace the functions and values that are lost from a wetland that is drained or filled. A replacement wetland should replace the same combination of functions and values provided by the impacted wetland. The evaluation of wetlands shall be performed in accordance with part 8420.540 of the Board of Water and Soil Resources Wetland Conservation Act Rules (August, 1993).
E. Wetland Replacement Standards:
1. General Requirements: The standards and guidelines in this subsection E shall be used in wetland creation and restoration efforts to ensure adequate replacement of wetland functions and values.
2. Specific Requirements: The standards in subsections E2a to E2h of this section shall be followed in all wetland replacements unless the technical evaluation panel determines that a standard is clearly not appropriate.
a. Water control structures must be constructed using specifications provided in the Minnesota Wetland Restoration Guide or their equivalent. Control structures may be subject to the department dam safety regulations.
b. Best Management Practices must be established and maintained adjacent to the entire perimeter of all replacement wetlands.
c. For replacement wetlands where the dominant vegetation of the wetland type identified as the replacement goal is not likely to recover naturally in a five (5) year period, wooded and shrub wetlands especially, the replacement wetland must be seeded or planted with appropriate species, as determined by the Soil and Water Conservation District, in coordination with the department. If the replacement wetland is seeded or planted, the seed or planting stock should be of local wetland origin to preserve local genotypes. During the monitoring period, the applicant must take reasonable steps to prevent invasion by any species, for example, purple loosestrife and Eurasian water milfoil, that would defeat the revegetation goal of the replacement plan.
d. Erosion control measures as determined by the Soil and Water Conservation District must be employed during construction and until permanent ground cover is established to prevent siltation of the replacement wetland or nearby water bodies.
e. For all restored wetlands where the original organic substrate has been stripped away and for all created wetlands, provisions must be made for providing an organic substrate. When feasible, the organic soil used for backfill should be taken from the drained or filled wetland.
f. The bottom contours of created types 3, 4, and 5 wetlands shall be undulating, rather than flat, to provide a variety of water depths.
g. Side slopes of created wetlands and buffer strip must not be steeper than five feet (5') horizontally for every one foot (1') vertically as averaged around the wetland. Side slopes of ten to one (10:1) to fifteen to one (15:1) are preferred.
h. Created wetlands shall have an irregular edge to create points and bays.
F. Monitoring: The purpose of wetland value replacement monitoring is to ensure that the replacement wetland achieves the goal of replacing lost functions and values.
G. Duration Of Monitoring: Monitoring shall be by means of an annual report as specified in subsection H of this section and shall continue for five (5) years following completion of the wetland replacement project. Through written notification to the applicant, the City may extend the required monitoring period for not more than an additional five (5) years if, at the end of the initial five (5) year period, the goal of the replacement plan has not been achieved, but may be achieved with more time.
H. Monitoring Annual Report:
1. Purpose: The purpose of the annual report is to describe actual wetland restoration or creation activities completed during the past year, activities planned for the upcoming year, and the information in subsection H2 of this section. The applicant shall submit the annual report to the City on a date determined by the City until the applicant has fulfilled all of the requirements of the City.
2. Report Content: The annual report shall include the following information and other site specific information identified by the City:
a. A description of the project location, size, current wetland type (Cowardin classification), and desired wetland type (goal);
b. A comparison of the as built specifications versus the design specifications (first annual plan only) and a rationale for significant changes;
c. Hydrology measurements: Seasonal water level elevations during the period April through October (msl or referenced to a known bench mark);
d. A list of the dominant vegetation in the wetland, including common names of the vegetation exceeding twenty percent (20%) coverage and an estimate of coverage, for example, fifty percent (50%) willow, twenty percent (20%) cattail, and thirty percent (30%) sedge; and
e. Color photographs of the project area taken anytime during the period June through August, referenced to the fixed photo reference points identified on the wetland replacement plan and labeled accordingly.
I. Monitoring Determinations By City: The City:
1. Will inspect the project when construction is complete and certify compliance with construction specifications, and may inspect the project at any time during the construction and monitoring period, and any time after that to assess the long term viability of the replaced wetland. When the City certifies that the construction specifications have been met, the City will so advise the applicant and return any bond or other security that the applicant had provided;
2. May order corrective action at any time during the required monitoring period if it determines that the goal of the approved replacement plan will not be met, and may require the applicant to prepare an amended wetland value replacement plan for review and approval by the City which describes in detail the corrective measures to be taken to achieve the goal of replacing lost wetland functions and values;
3. Shall make a finding based on a site visit at the end of the monitoring period as to whether the goal of the replacement plan has been met. If the goal of the replacement plan has not been met, the City will order corrective action and extend the monitoring period; and
4. Will require one or more of the following actions if, during the monitoring period, the City finds that the goal of the replacement plan will not be met:
a. Order the applicant to prepare and implement a new replacement plan;
b. Issue a cease and desist order on the draining and filling activity if it has not been completed;
c. Order restoration of the impacted wetland;
d. Obtain forfeiture of a bond or other security and use the proceeds to replace the lost wetland values;
e. Ask the District Court to order the applicant to fulfill the replacement plan; or
f. Other actions that the City determines necessary to achieve the goal of the replacement plan. (Prior Code § 20-93-14)