A.
Purpose. The purpose of this district is to preserve and enhance land for agricultural uses, and to incorporate and apply the livestock facility siting law requirements found in §§ 92.16 and 93.90, Wis. Stats., and ATCP 51 of the Wisconsin Administrative Code and to regulate the siting of new livestock facilities (with an excess of 500 animal units) and the expansion of existing livestock facilities by more than 20% (and over 500 animal units) in the Farmland Preservation Zoning District within the Town of Ledgeview.
B.
Authority. This article is adopted pursuant to the Town's zoning powers found in §§ 60.62, 62.23(7), 92.16 and 93.90, Wis. Stats., together with the administrative provisions set forth in Ch. ATCP 51 of the Wisconsin Administrative Code, inclusive of all future amendments to any provisions of these statutes and administrative rules. The livestock facility siting standards established in Ch. ATCP 51, Wis. Adm. Code, including all appendixes, worksheets, and any future amendments to that chapter, are incorporated by reference and adopted.
C.
Incorporation of state law. Pursuant to the provisions of §§ 93.90, Wis. Stats., the Town of Ledgeview does hereby adopt and incorporate into its existing Zoning Ordinance the provisions of §§ 92.16 and 93.90, Wis. Stats., and Ch. ATCP 51 of the Wisconsin Administrative Code, inclusive of all future amendments to any provisions of § 93.90, Wis. Stats. and Ch. ATCP 51 of the Wisconsin Administrative Code. The Town of Ledgeview's Zoning Ordinance hereby reflects the provisions of §§ 92.16 and 93.90, Wis. Stats., and Ch. ATCP 51 of the Wisconsin Administrative Code as if said statutory and administrative provisions were set forth in their entirety within the text of the Town's Zoning Ordinance.
D.
Findings. The livestock siting, animal waste storage, and contaminated runoff storage facilities regulations and standards created by the Town are based upon the following reasonable and scientifically defensible findings of fact which are adopted and incorporated herein by reference:
(1)
The Town recognizes the importance of protecting groundwater quality, and that proper land use and management, including proper management of nutrients from livestock operations, is essential to the protection of groundwater quality, public health, safety and welfare, and the property tax base of the Town. Many of the Town's residents rely on private wells for their drinking water.
(2)
Improper storage of livestock waste and land application of such wastes can significantly impact groundwater quality by increasing the level of nitrates and increasing the risk of pathogens and other contaminants, particularly in environmentally vulnerable areas.
(3)
Nitrates, pathogens, and other contaminants present significant environmental and public health risks. Scientific research shows that elevated concentrations of nitrate in drinking water has been associated with the risk of methemoglobinemia, or "blue baby syndrome," in humans, and other human health risks. Contaminated groundwater directly threatens the health of Town residents, many of whom rely on private wells for their water supply.
(4)
The Town lies in the contact of the Silurian bedrock and underlying Maquoketa shale. This area is characterized by a dense and universal fracture network, shallow soil surface, and little surface runoff, allowing water to easily infiltrate to the subsurface. Recharge is exceedingly rapid and carries surface contaminants to the water table. Flow within the aquifer occurs primarily along bedding plane fractures with little to no reduction of contaminants within the aquifer. This type of a geologic setting makes the area extremely vulnerable to groundwater contamination, especially for shallower private wells. Source: Presentations of UW-Oshkosh Geology Professor Dr. Maureen Muldoon and USDA Agricultural Researcher Dr. Mark Borchardt to the Town of Ledgeview Town Board, May 29, 2018, https://www.ledgeviewwisconsin.com/govenrment/departments/community- developmentbuilding-inspection/zoning-and-planning/adopted-plans-documents-maps/; Kevin Erb, Eric Ronk, Vikram Koundinya, and John Luczaj, Groundwater Quality Changes in a Karst Aquifer of Northeastern Wisconsin, USA: Reduction of Brown Water Incidence and Bacterial Contamination Resulting from Implementation of Regional Task Force Recommendations, Resources 2015, 4, 655-672; doi:10.3390/resources4030655; K. Erb and R. Stieglitz, Final Report of the Northeast Wisconsin Karst Task Force, February 9, 2007.
(5)
Sampling results from Calumet County, an area of the state with a geology of shallow fractured bedrock similar to that in the Town, indicated that:
(a)
Thirty-five percent of wells sampled were positive for coliform bacteria;
(b)
4.6% of wells sampled were positive for E. coli.
(c)
Twenty-five percent of wells sampled were above the health standard of 10 ppm for nitrate.
(d)
Twenty-eight percent of wells sampled exhibited elevated levels of nitrate (2-10 ppm).
(e)
Forty-seven percent of wells sampled were found to be unsafe for either bacteria or nitrate.
(f)
Twelve percent of wells sampled were found to be unsafe for both bacteria and nitrate.
Source: K. Erb and R. Stieglitz, Final Report of the Northeast Wisconsin Karst Task Force, February 9, 2007. |
(6)
There is a rapid interconnection between surface waters and groundwater in areas with shallow fractured bedrock features such as the Town. This interconnection means that surface water contamination due to livestock waste runoff can quickly lead to groundwater contamination. Source: K. Erb and R. Stieglitz, Final Report of the Northeast Wisconsin Karst Task Force, February 9, 2007; Presentation of UW-Oshkosh Geology Professor Dr. Maureen Muldoon to the Town of Ledgeview Town Board, May 29, 2018, https://www.ledgeviewwisconsin.com/government/departments/community-developmentbuilding-inspection/zoning-and-planning/adopted-plans-documents-maps/.
(7)
Researchers have found an association between the proximity of animal waste storage facilities such as manure lagoons and the presence of coliform bacteria (i.e., E. coli) and nitrates in drinking water. There is a significant likelihood of high nitrates and coliforms within 2,500 feet of a waste storage facility or landspreading field. The chance that a drinking water well or surface water will be contaminated does not fall below the statewide average until the distance from a waste storage facility exceeds 5,000 feet. Source: Presentation of USDA Agricultural Researcher Dr. Mark Borchardt to the Town of Ledgeview Town Board, May 29, 2018, https://www.ledgeviewwisconsin.com/government/departments/community-developmentbuilding-inspection/zoning-and-planning/adopted-plans-documents-maps.
(8)
Researchers have concluded that one mechanism for preventing exposure to manure-borne pathogens is minimizing transport by increasing the distance between livestock and manure storage lagoons and waterways and wells. Source: Presentation of USDA Agricultural Researcher Dr. Mark Borchardt to the Town of Ledgeview Town Board, May 29, 2018, https://www.ledgeviewwisconsin.com/government/departments/community-developmentbuilding-inspection/zoning-and-planning/adopted-plans-documents-maps/.
(9)
Setback requirements are an essential element of managing separation distance between livestock structures, neighboring residences, and groundwater wells. Source: The Report of the Livestock Facility Siting Technical Expert Committee Recommendations, December 21, 2010.
(10)
Separation distance is an effective tool for reducing impacts on neighbors, including for odor management and water quality purposes. For purposes of odor management, odors are far less noticeable at 800 feet than they are at 400 feet. Source: Final Report On Wisconsin's Dairy And Livestock Odor And Air Emission Project, September 2009.
(11)
The location of livestock operations also has a significant negative impact on property values. Source: John A. Kilpatrick, Concentrated Animal Feeding Operations and Proximate Property Values, Appraisal Journal, pages 301 through 306, July 1, 2001.
(12)
Given the vulnerable geology in the Town, land use and management regulations beyond the performance standards, prohibitions, conservation practices and technical standards contained in § 281.16(3), Wis. Stats., and Ch. NR 151, Wis. Adm. Code, and regulations more stringent than state standards contained in § 93.90(2)(a), Wis. Stats., are necessary to achieve or maintain water quality standards and to protect public health and safety.