A. 
Natural resource protection standards. All new certified survey maps, subdivision plats, or condominiums created in the Town of Barton shall comply with the natural resource protection standards set forth in Table 4. All the natural resources required to be protected under this article shall remain undisturbed and in a natural state except those natural resources where mitigation is permitted and such mitigation is in strict accord with those requirements set forth in this article of this chapter.[1]
Table 4
Natural Resource Protection Standards
Natural Resource Feature
Zoning District Type
Agricultural
Residential
Nonresidential
Protection Standard
Mitigation Permitted
Protection Standard
Mitigation Permitted
Protection Standard
Mitigation Permitted
Steep slopes:
10% to 19%
0%
N/A
60%
No
40%
No
20% to 30%
65%
No
75%
No
70%
No
+30%
90%
No
85%
No
80%
No
Woodlands and forests(a):
Mature
70%
No
70%
No
70%
Yes
Young
50%
No
50%
Yes
50%
Yes
Lakes and ponds
100%
Yes
100%
Yes
100%
Yes
Streams
100%
No
100%
Yes
100%
Yes
Shore buffer(a)
100%(a)
No
100%(a)
No
100%(a)
No
Floodplains/ floodlands(b)
100%
No
100%
No
100%
Yes
Drainageways
30%
Yes
30%
Yes
30%
Yes
Wetlands and shoreland wetlands(a)
100%
No
100%
No
100%
Yes
NOTES:
(a)
As regulated by Chapter 23, Shoreland, Wetland and Floodplain Zoning, of the Washington County Code, as amended.
(b)
As regulated by Chapter 23, Shoreland, Wetland and Floodplain Zoning, of the Washington County Code, as amended.
N/A = Not applicable.
[1]
Editor's Note: Amended at time of adoption of Code (see Ch. 1, General Provisions, Art. II).
B. 
Natural resource features determination.
(1) 
Steep slopes. The definition of "steep slopes," as applied to this article, appears in Article XV of this chapter.
(a) 
Steep slopes are to be determined through the use of the following sources and/or methods in the order indicated below. If the first source is considered inaccurate or inappropriate, as determined by the Plan Commission, the succeeding source shall be used:
[1] 
Topographic survey prepared by and certified by a Wisconsin registered land surveyor at a contour interval of not less than two feet.
[2] 
Large-scale one inch equals 200 feet Washington County topographic maps.
[3] 
USGS 7.5-minute topographic quadrangle maps.
(b) 
The area of steep slopes (in square feet or acres) shall be measured and graphically delineated on a topographic drawing and on the natural resource protection plan. Such steep slope drawing shall graphically indicate those steep slope areas, by slope type, of the property pursuant to the "steep slope" definition set forth in Article XV of this chapter.
(2) 
Woodlands and forests. The definitions of "woodlands" and "forests" (mature and young), as applied to this article, appear in Article XV of this chapter.
(a) 
The determination of woodland and forest boundaries shall be based on the following sources:
[1] 
One inch equals 400 feet aerial photographs prepared by the Southeastern Wisconsin Regional Planning Commission (SEWRPC) and available from either SEWRPC or from Washington County (most recent date only).
[2] 
A field survey of trees compiled by a registered land surveyor and identified by a landscape architect, forester, arborist, or botanist with a professional degree in one of those fields of endeavor.
(b) 
The area of woodlands and forests (mature and young), in square feet or acres, shall be measured and graphically delineated on the natural resource protection plan. Such woodland and forest area drawing shall indicate all woodland and forest areas of the property. The location, size, and species of all healthy trees having a diameter of eight inches or greater DBH that are located in woodland and forest areas within 25 feet of any proposed improvement and/or in woodland and forest areas to be demolished due to the placement of improvements or grading are to be graphically shown on the natural resource protection plan or submitted as a separate drawing. For the remaining undisturbed areas of the certified survey map, subdivision plat, or condominium, only the outline of woodland and forest areas indicating whether they are mature or young woodlands is required.
(3) 
Lakes and ponds.
(a) 
Lakes and ponds, as defined in Article XV of this chapter, are to be determined through the use of the definitions of "lake" and "pond" as set forth in Article XV of this chapter and the sources in the order indicated below. If the first source is considered inaccurate or inappropriate, as determined by the Plan Commission, the succeeding source shall be used:
[1] 
Topographic survey prepared by and certified by a Wisconsin registered land surveyor at a contour interval of not less than two feet.
[2] 
Large-scale one inch equals 200 feet Washington County topographic maps.
[3] 
USGS 7.5-minute topographic quadrangle maps.
(b) 
The area of lakes and ponds (in square feet or acres) shall be measured and graphically delineated on the natural resource protection plan.
(4) 
Streams.
(a) 
Streams, as defined in Article XV of this chapter, are to be determined through the use of the definitions of "channel" and "stream" as set forth in Article XV of this chapter and the sources in the order indicated below. If the first source is considered inaccurate or inappropriate, as determined by the Plan Commission, the succeeding source shall be used:
[1] 
Topographic survey prepared by and certified by a Wisconsin registered land surveyor at a contour interval of not less than two feet.
[2] 
Large-scale one inch equals 200 feet Washington County topographic maps.
[3] 
USGS 7.5-minute topographic quadrangle maps.
(b) 
The area of streams (in square feet and acres) shall be measured and graphically delineated on the natural resource protection plan.
(5) 
Shore buffers.
(a) 
Shore buffers, as defined in Article XV of this chapter, are to be determined as the land within 75 feet of the ordinary high-water mark of all navigable waters and parallel to that ordinary high-water mark. Navigable waters are to be determined through the use of the definition of "navigable water" set forth in Article XV of this chapter and the sources in the order indicated below. If the first source is considered inaccurate or inappropriate, as determined by the Plan Commission, the succeeding source shall be used:
[1] 
Topographic survey prepared by and certified by a Wisconsin registered land surveyor at a contour interval of not less than two feet.
[2] 
Large-scale one inch equals 200 feet Washington County topographic maps.
[3] 
USGS 7.5-minute topographic quadrangle maps.
(b) 
The area of shore buffers (in square feet and acres) shall be measured and graphically delineated on the natural resource protection plan.
(6) 
Floodplain/floodlands. The definitions of "floodplain" and "floodlands" appear in Article XV of this chapter. The one-hundred-year recurrence interval floodplain and floodways shall be determined as depicted on the Federal Emergency Management Agency's (FEMA) FIRM [Flood Insurance Rate Map(s)], with the effective date of September 1, 1983, as amended. Where a conflict exists between the floodland limits as shown on the Federal Emergency Management Agency's (FEMA) FIRM [Flood Insurance Rate Map(s)] and actual field conditions, the elevations from the one-hundred-year recurrence interval flood profiles contained in the published Flood Insurance Study - Washington County, Wisconsin (Unincorporated Areas), prepared by the Federal Emergency Management Agency (FEMA), dated March 1, 1983, shall be used.
(7) 
Drainageways. Drainageways, as defined in Article XV of this chapter, are to be determined as the land on either side of and within 50 feet of the center line of any intermittent or perennial stream graphically shown on those maps cited below, except for areas designated as wetlands, shoreland wetlands, floodlands, floodways, or one-hundred-year recurrence interval floodplains.
(a) 
Drainageways are to be determined through the use of the following sources and/or methods in the order indicated below. If the first source is considered inaccurate or inappropriate, as determined by the Plan Commission, the succeeding source shall be used:
[1] 
Topographic survey prepared by and certified by a Wisconsin registered land surveyor at a contour interval of not less than two feet.
[2] 
Large-scale one inch equals 200 feet Washington County topographic maps.
[3] 
USGS 7.5-minute topographic quadrangle maps.
(b) 
The area of drainageways (in square feet and acres) shall be measured and graphically delineated on the natural resource protection plan.
(8) 
Wetlands (including shoreland wetlands).
(a) 
"Wetlands" and "shoreland wetlands" are defined in Article XV of this chapter. Wetland areas shall be determined by reference to the following sources in the order shown below. If the first source is considered inaccurate or inappropriate as determined by the Plan Commission, the second technique may be used:
[1] 
Wetland inventory maps prepared for the Town of Barton as part of the "Wisconsin Wetland Inventory" prepared by the Wisconsin Department of Natural Resources, as amended.
[2] 
Field survey of plant material by a botanist with a professional degree in either botany or biology.
(b) 
The area of wetlands and/or shoreland wetlands (in square feet and acres) shall be measured and graphically delineated on the natural resource protection plan.
C. 
Natural resources measurement. All land area within a proposed certified survey map, subdivision plat, or condominium consisting of the natural resource features defined in this chapter shall be accurately measured. The total square feet and acreage of each natural resource feature shall be multiplied by its respective natural resource protection standard as set forth in Table 4, "Natural Resource Protection Standards," of this chapter to determine the amount of each natural resource feature to be protected by a conservation easement. If two or more natural resource features are present on the same area of land, only the most restrictive natural resource protection standard shall be used. (For example, if floodlands and woodlands and forests occupy the same space on a site, the natural resource protection standard would be 100% for this area, representing the higher of the two standards.) Those areas to be demolished due to improvements or site grading or disturbed through the application of permitted mitigation techniques shall also be measured and so noted but shall not be counted as a natural resource area to be preserved.
A. 
Intent of mitigation. The Town of Barton recognizes that, under certain circumstances, property owners, subdividers, or condominium developers may wish to develop in portions of those protected natural resource feature areas indicated in Table 4 that are shown as eligible for mitigation. In Subsection B of this section, the conditions for mitigation and mitigation standards are set forth for the various natural resource features for which mitigation is allowed under the provisions of Table 4. The intent of this section is not to permit greater destruction of natural resource features than is permitted under the requirements of this chapter for typical property or development. This section sets specific standards for use when the extent of the natural resources on a site and the use of the regulations would create a major hardship for said natural resource feature protection. Thus, mitigation is intended to be used in lieu of a variance request when severe hardships would result from the strict enforcement of the natural resource protection standards and requirements set forth in this chapter.
B. 
Mitigation standards. The following methods, requirements, standards and/or criteria shall be followed for the mitigation of those natural resource features that may be mitigated under the requirements set forth under Table 4:
(1) 
Woodlands and forests. Either of the following two alternative requirements shall be applicable to the mitigation of woodland and forest areas:
(a) 
Alternative 1.
[1] 
Mitigation shall include the planting of 1.25 acres of new woodland/forest for every one acre of disturbed woodland/forest for which mitigation is required.
[2] 
Mitigation shall include the replacement of woodlands/forests that have been disturbed. Such mitigation shall consist of the planting of new woodland/forest areas, as specified in Subsection B(1)(a)[1] above, using the following number of plants per acre of mitigated area:
15 canopy trees, minimum 3.5-inch caliper*
12 canopy trees, minimum 2-inch caliper*
250 canopy trees, minimum 4-foot-high whips
50 understory trees, minimum 5-foot-high whips
25 shrubs, minimum 12 inches high
*NOTE: Each 3.5-inch-caliper canopy tree may be substituted with two 1.5-inch-caliper canopy trees.
(b) 
Alternative 2.
[1] 
Mitigation shall include the planting of 1.50 acres of new woodland/forest for every one acre of disturbed woodland/forest for which mitigation is required.
[2] 
Mitigation shall include the replacement of woodlands/forests that have been disturbed. Such mitigation shall consist of the planting of new woodland/forest areas, as specified in B(1)(b)[1] above, using the following number of plants per acre of mitigated area:
12 canopy trees, minimum 3.5-inch caliper*
10 canopy trees, minimum 2-inch caliper*
200 canopy trees, minimum 4-foot-high whips
40 understory trees, minimum 5-foot-high whips
20 shrubs, minimum 12 inches high
*NOTE: Each 3.5-inch-caliper canopy tree may be substituted with two 1.5-inch-caliper canopy trees.
(c) 
The species of plants to be used in the mitigation of woodlands/forests shall be similar to those that are destroyed, and a minimum mix of six species are to be planted. Acceptable species for woodland and forest mitigation are as indicated in Table 5. No more than 80% of the total number of trees planted for mitigation purposes, however, shall be of the sugar maple (Acer saccharum) species.
Table 5
Tree Species for Woodland and Forest Mitigation
Species Common Name
Species Scientific Name
Sugar maple
Acer saccharum
Bitternut hickory
Carya cordiformis
Hackberry (sugarberry)
Celtis occidentalis
Butternut
Juglans cinerea
Black walnut
Juglans nigra
Eastern hophornbeam
Ostrya virginiana
Black cherry
Prunus serotina
White oak
Quercus alba
Red oak
Quercus borealis
American basswood
Tilia americana
American elm
Ulmus americana
Slippery elm
Ulmus rubra
(d) 
The land upon which the mitigation is to take place shall be protected with a deed restriction and conservation easement as a permanent natural resource features conservation easement.
(e) 
No tree cutting or removal, subsequent to the adoption of this chapter, shall reduce the woodland/forest natural resource features protection requirements of this chapter.
(2) 
Lakes and ponds. As may be permitted under the requirements of Chapter 23, Shoreland, Wetland and Floodplain Zoning, of the Washington County Code, as amended. Where permitted under the requirements of Chapter 23 of the Washington County Code, as amended, the required lakes and ponds natural resource protection standard may be reduced and/or mitigated only if such reduction and/or mitigation is part of a Town Engineer approved stormwater drainage system that meets, at a minimum, all of the following criteria:
(a) 
The time of concentration of stormwater flows remains unchanged or is lengthened.
(b) 
Stormwater storage capacity is unchanged or increased.
(c) 
Additional water is not backed up onto adjoining properties.
(3) 
Floodplains and floodlands. As may be permitted under the requirements of Chapter 23, Shoreland, Wetland and Floodplain Zoning, of the Washington County Code, as amended.
(4) 
Drainageways. The required drainageway natural resource protection standard may be reduced and/or mitigated only if such reduction and/or mitigation is part of a Town Engineer approved stormwater drainage system that meets, at a minimum, all of the following criteria:
(a) 
The time of concentration of stormwater flows remains unchanged or is lengthened.
(b) 
Stormwater storage capacity is unchanged or increased.
(c) 
Vegetation is installed stabilizing the drainageway soil.
(d) 
The resultant drainageway produces less stormwater velocity than preexisted or reduces stream bank erosion through the provision of erosion control measures.
(e) 
Additional water is not backed up onto adjoining properties.
(5) 
Wetlands and shoreland wetlands. As may be permitted under the requirements of Chapter 23, Shoreland, Wetland and Floodplain Zoning, of the Washington County Code, as amended. In addition, a permit from the United States Army Corps of Engineers pursuant to the requirements of Section 404 of the Clean Water Act (33 U.S.C. § 1344) shall be submitted to the Town of Barton certifying that filling has been approved and permitted by the Corps, as a condition of Town review.
C. 
Off-site mitigation. Off-site mitigation may be permitted by the Plan Commission, provided that such off-site mitigation occurs within the same subwatershed as the natural resource feature, or property, being mitigated.