Chapter 8: Environmental
Features Profile
This chapter profiles the environmental features of
The Soil Survey of Leelanau
County describes the Township's topography as ranging from level to gently
sloping to steep. United States Geological Survey (USGS) maps provide contour
data in 5- meter intervals, as well as spot elevations. Land elevations depicted by USGS range from
179 meters to 306 meters above sea level. The lowest point of surface elevation
is found at the intersection of
Map 3 depicts the township's
terrain in 25-meter intervals. Generally, the lowest elevations are found along
the shorelines. Elevation increases gradually increase from east to west. The
topographic change from west to east is more dramatic. This graphic depicts two
distinct hills extending through the western portion of the township.
The hilly terrain found in
First, steep slopes, defined as those over 15%, can erode more easily when the soil is exposed. The result of soil erosion can be sediment pollution of lakes and streams and ugly scars on the land. In severe cases of erosion, property damage can result as roads or buildings are covered by windblown sand; fertile soil is lost in agricultural areas by either wind or water erosion; and roads are washed out or foundations undercut by water erosion.
Second, development on ridges is highly sought for the spectacular views, but unless carefully done, is also highly visible from the valleys, potentially changing scenic character and affecting tourism.
Both water and wind are erosive
agents in
The management practice that best protects steep slopes from erosion and, as a result, lake and stream water quality, is complete, vegetative cover. If clearing of vegetation is necessary, it is important to employ erosion control methods. Primary erosion control methods include:
· Disturb the smallest area possible during development.
· Use temporary erosion control and sedimentation prevention methods during development.
· Leave exposed soils bare for the shortest time possible.
· Quickly establish vegetative cover on disturbed areas.
· Avoid development on steep slopes.
In general, topography provides a practical guide for land development decisions. For example, a structure located on a hilltop may be susceptible to wind damage while a structure located at the base of a hill may be subject to flooding. Construction on steep slopes may increase the risk of soil erosion and slope failure. In addition, most hillside construction guidelines emphasize the need to minimize grading on slopes and to avoid disturbing slopes steeper than 35 percent. Generally, construction on slopes with inclines greater than 12 percent should be limited and road construction should parallel slope contours. Good hillside development has been characterized as follows: "When completed, development should not dominate the landscape. The development should instead appear to be a natural hillside, with homes randomly scattered."[1]
There are four major soil
associations present in
Ø Emmet-Omena: Covers the entire northwest quadrant and primarily western portions of the northeast quadrant of the township. This soil association consists mainly of well- drained, nearly level to very steep, loamy soils on moraines.
Ø
Leelanau-Mancelona: Forms a narrow band along
the
Ø
Emmet-Leelanau: Found in the southern half of
the Township away from the
Ø
East Lake-Eastport-Lupton: Covers the entire
Village of Suttons Bay and nearly all of Section 31 in the Township. In
addition, a narrow band stretches between the
The characteristics of specific soil series within these associations defines the capacity of the land to support certain types of uses. Soils most suitable for development purposes are well-drained and not subject to a high water table. Adequate drainage is important to minimize storm water impacts and to ensure the efficient operation of septic drain fields. Adequate depth to the water table is necessary to prevent water contamination from septic systems. A high water table also may limit the construction of basements. Though civil engineering techniques can be employed to improve drainage and maintain adequate separation from the water table, such techniques are expensive to construct and maintain.
Table 23 details the specific
soil series within
As shown on Table 23, there is much variation in relation to soils posing constraints to the development of on-site septic disposal systems. The primary difficulties are poor filtering capacity and wetness/flooding. A majority of the soils which overlay the township pose slight to moderate constraints to the construction of residential and commercial structures. Severe constraints to construction are primarily due to slopes in excess of 12 percent incline and wet soils.
Soils also play an important role in the food supply system. The SCS has identified soils that are well or uniquely suited to crop production. When considering future land use decisions, it is important to consider the value of certain soils for agricultural purposes. Once a soil is developed or used for a non-agricultural purpose, it is permanently altered and its utility for agricultural production is greatly diminished, if not destroyed. Although the agricultural industry is in decline, development which threatens this non-renewable resource should be carefully considered. Areas which are considered prime or unique for agricultural use are depicted on Map 5.
Prime farmland is defined by the U.S. Department of Agriculture as "land that has the best combination of physical and chemical characteristics for producing food, forage, fiber, and oil seed crops. It could be cropland, pasture, range, forest, or other land but it does not include urban or built-up land or water areas. The soil qualities, growing season, and moisture supply are those needed for well managed soil to produce sustained yields."[2]
|
Table 23 |
||
|
Soil Series and Symbol |
Septic Development Constraints |
Residential or Commercial Construction Constraints |
|
Alcona (AlC) |
Slight |
Slight |
|
Eastport (EdB) |
Slight |
Slight |
|
Kalkaska (KaB, KaE, KaF) |
Slight for slopes 0 to 12 percent (KaB), Severe for
slopes 18 to 45 percent (KaE and KaF). |
Slight-moderate; Severe on slopes of greater than 12
percent incline |
|
|
Slight |
Slight |
|
Bach (Ba) |
Severe |
Severe |
|
Emmet-Leelanau Complex (EnA, EnB, EnC, EnD, EnE,
EnF) |
Slight for slopes 0 to 12 percent (Ena, EnB, EnC);
moderate for slopes 12 to 18 percent (EnD); and severe for slopes 18 to 50
percent (EnE and EnF). |
Slight-moderate; Severe on slopes of greater than 12
percent incline |
|
Emmet-Omena (EsA, EsB, EsC, EsD, EsF) |
Slight for slopes 0 to 12 percent (EsA, EsB, EsC);
moderate for slopes 12 to 18 percent (EsD); and severe for slopes 18 to 50
percent (EsF). |
Slight-moderate; Severe on slopes of greater than 12
percent incline |
|
Emmet-Mancelona (EoC, EoD, EoE) |
Slight for slopes 0 to 12 percent (EoC); moderate
for slopes 12 to 18 percent (EoD); and severe for slopes 18 to 50 percent
(EoE). |
Slight-moderate; Severe on slopes of greater than 12
percent incline |
|
|
Slight for slopes 0 to 12 percent (LlC); moderate
for slopes 12 to 18 percent (LlD); and severe for slopes 18 to 50 percent (LlE
and LlF). |
Slight-moderate; Severe on slopes of greater than 12
percent incline |
|
Lupton-Markey (Lm) |
Severe |
Severe |
|
Kiva-Mancelona (KmC, KmD, KmE) |
Slight for slopes 2 to 12 percent (KmC) moderate for
slopes 12 to 18 percent (KmD); and severe for slopes 18 to 25 percent (KmE) |
Slight-Moderate; Severe on slopes of greater than 12
percent incline |
|
Roscommon-Markey (Rm) |
Severe |
Severe |
|
Alcona-Richter (ArA, ArB) |
Slight |
Slight |
|
Mancelona (MdB, MdC) |
Slight |
Slight |
|
Mancelona-Richter (MrB) |
Slight |
Slight |
|
|
Slight for slopes 0 to 12 percent (MlC); Severe for
slopes 18 to 45 percent (MlE, MlF). |
Slight; Severe on slopes of greater than 12 percent
incline |
|
Nester (NsB, NsC) |
Severe |
Severe |
|
Alpena (AsC) |
Slight |
Slight |
|
Hettinger-Tonkey (Ht) |
Severe |
Severe |
|
Wind Eroded Land (WlC, WlD) |
Too variable for determination |
Too variable for determination |
|
Tonkey-Munuscong-Iosco (TmA, TmB) |
Severe |
Severe |
|
Au Gres-Kalkaska (AuA) |
Severe |
Severe |
|
Kalkaska (KaC, KaD) |
Slight for slopes 0 to 12 (KaC) and Moderate for
slopes 12 to 18 percent. |
Slight-Moderate; Severe on slopes of greater than 12
percent incline |
|
Detour (DtB) |
Severe |
Severe |
|
Deer Park-Roscommon (DB) |
Slight |
Slight |
|
Iosco-Epoufette (Ie) |
Severe |
Severe |
|
|
Slight for slopes 0 to 12 percent (EaB); moderate
for slopes 12 to 18 percent (EaC); and severe for slopes 18 to 25 percent
(EaD). |
Slight-moderate; Severe on slopes of greater than 12
percent incline |
|
Richter-Alcona (RaB) |
Severe |
Severe |
|
|
Too variable for determination |
Too variable for determination |
|
Lake Beaches (Lb) |
Too variable for determination |
Too variable for determination |
|
Hettinger (Hm) |
Severe |
Severe |
|
Wallace-Kalkaska (WkC) |
Moderate |
Slight-Moderate |
|
Adrian-Houghton (Ah) |
Severe |
Severe |
|
Sanilac (SnB) |
Severe |
Severe |
|
|
Moderate |
Slight-Moderate; Severe on slopes of greater than 12
percent incline |
|
Source: Soil Survey of |
||
Hydrological Features
To protect the public's right to
boat, fish, swim, and enjoy inland lakes, the state regulates construction
activities within inland waters under the
Ø Construction of a structure or the operation of a marina;
Ø Creation or modification of an inland lake or stream;
Ø Interference with the natural flow of a stream or lake; and
Ø Dredging or filling of a stream or lake.
Activities permitted without a permit include installing a seasonal, noncommercial dock, and the reasonable sanding of beaches.
Pollutants
and the velocity of stormwater runoff affect water quality. Pollutants occur in four forms: sediment,
chemicals, pathogens, and warm water.
Sediment comes from bare soil, other erosion sites, and paved
surfaces. It can destroy fish
habitat. Sediment also carries chemical
pollutants although these can be carried by stormwater runoff alone. Chemical pollutants include nutrients such as
phosphorus and nitrogen; toxic materials such as oils, pesticides, and salts;
and changed water chemistry, such as lowered or raised pH. Nutrients can increase nuisance aquatic plant
growth. Toxic materials and changed
water chemistry can kill animals in the water and be a human health
hazard. Pathogens include bacteria and
viruses that come from animal waste and untreated or improperly treated sewage
from homes and businesses and can be a serious human health hazard. Warmed water, such as the stormwater runoff
that travels over paved surfaces and lawns before entering lakes and streams
can change the temperature of the stream, affecting aquatic life. It can also damage fish populations.
Applications of fertilizers, pesticides and herbicides to watershed lands affects water quality when it runs off the land. These pollutants originate on croplands, livestock pens, orchards, golf courses, shore-side lawns and gardens.
The shoreline ecosystem is subject to damage through clearing or trampling of vegetation that holds the sand in place. The result of development in this area or of vegetative clearing could be wind erosion, structural damage or loss, damage to drives and roads, loss of wildlife habitat, and loss of scenic character.
There are a three major
drainageways in
The Soil Erosion and Sedimentation Control Act, Public Act 347 of 1972, protects lakes and streams from sedimentation. The Act requires a permit for any new construction within 500 feet of a lake or stream or any major construction that will open up more than one acre of land.
Wetlands are complex ecological
systems that function in a number of beneficial ways. Wetlands reduce flood
hazards by providing additional storm water storage. Wetlands that overlay
groundwater recharge areas improve groundwater quality by filtering the water
as it percolates through the soil. Wetlands located along a watercourse protect
surface water quality by filtering surface water run-off. Finally, wetlands are
highly productive ecosystems which provide an essential habitat to much of
Pockets of wetland area are found
in conjunction with the township drainageways. Map 6 depicts the location of
wetlands in
The Goemaere-Anderson Wetland Protection Act, Public Act 203 of 1979, as amended, was enacted to protect wetlands by restricting their use to certain activities (such as fishing, farming, among others) while permitting other activities only after permission and approval by the Michigan Department of Environmental Quality (MDEQ). Permits are approved based on a review of an environmental assessment filed by the petitioner and upon the finding that the activity is in the public interest. Under the Wetland Protection Act, the following wetlands are protected:
Ø
Those that are contiguous to an inland lake,
pond, river, stream or similar natural watercourses, or one of the
Ø Those that are five acres or larger in area and located in counties which contain a population of at least 100,000 people.
Development within wetland areas should be avoided. The filling of wetlands as part of development plans should also be avoided, or at least minimized. Ideally, structures should be set back from wetlands and a natural vegetative buffer strip maintained within the setback area.
Woodlands in
Woodlands in
Woodland areas are complex ecological systems and, consequently, provide multiple benefits to the environment and its wildlife and human inhabitants. Woodlands play a role in flood protection by slowing the flow of surface run-off to allow for greater storm water infiltration. Woodlands also reduce air pollutants by absorbing certain air borne pollutants. In addition to providing wildlife habitants, forest vegetation moderates the effects of winds and temperatures while stabilizing and enriching the soil. For human inhabitants, forested areas offer a visual and audio barrier which is considered aesthetically pleasing and offer unique opportunities for recreation and relaxation.
Woodland resources contribute greatly to the Township's environmental quality. The conservation of woodlots will play a positive role in maintaining and enhancing the future environmental character of the township. Woodland areas should be conserved, as possible. Trees which are removed through development actions should be replaced. Of special concern will be the fragmentation of woodland areas through parcel divisions in and adjacent to wooded areas.
The Michigan Natural Features
Inventory (MNFI) database is part of the Natural Heritage Program of the
MDNR-Wildlife Division. The MNFI inventories the location of special natural
features such as
The presence of listed species does not necessarily preclude development but may require a development plan which is sensitive to the conservation of the feature. However, if an endangered species is to be taken or harmed, a permit is required from the state.
Because the MNFI database is still undergoing development, it is likely that there are gaps in the data. A lack of information should not be interpreted as a lack of special features. In some cases, the best means for determining the status of natural features will be to have a biological survey completed. Finally, it is also expected that the MNFI database information will need to be revised and updated as plant and animal communities evolve and change. Periodic reviews of local database information is recommended.
Environmental hazards
A database search was conducted
by EcoSearch Environmental Resources to provide the location and type of
environmental hazards which may exist in
One
RCRA sites cover both treatment, storage, and disposal facilities (TSD) and large and small quantity generators. The generators database, which identified Frigid Foods, is a subset of the complete national Resource Conservation and Recovery Information System (RECRIS) which includes hazardous waste generators which create more than 100kg of hazardous waste per month or meet other requirements of RCRA.
The Comprehensive Environmental Response, Compensation, and Liability Information System (CERCLIS) maintains information on over 15,000 sites nationally identified as hazardous or potentially hazardous which may require action. These sites are currently being investigated or an investigation has been completed regarding the release of hazardous substances. Frigid Foods was also matched in this database system.
Two
Radon is an invisible, odorless, naturally occurring radioactive gas produced by decaying uranium in the ground. Radon (which is suspected of causing lung cancer) can enter a structure through foundation cracks or well water. Though radon occurs naturally, exposure to radon has only recently become a concern. Radon may accumulate in tightly sealed structures that have limited fresh air exchanges such as newer, energy efficient homes. Dangerous levels of accumulated radon pose a health risk on par with one or two packs of cigarettes a day. The United States Environmental Protection Agency (USEPA) considers radon concentrations below 4 picocuries per liter of air (pCi/L) safe.
Area radon information, which is
tabulated by county, has been collected by the USEPA for radon zones in