HomeMy WebLinkAboutSection 2: Physical Environment
2.0 Section 2 - Physical Environment
2.1 Topography and Geology
St. Joseph and the surrounding area has a moderately flat topographic relief,
with elevations ranging from approximately 1,060 - 1,150 feet above mean
sea level. In the study area, there is a watershed divide between the Watab
and Sauk Rivers that runs from the southwest to the northeast (Figure 2).
Runoff from the northwest area is toward the Watab River and from the
southeast area is toward the Sauk River,
Geology in the St. Joseph area is formed by material of three different broad
geologic types that were deposited over many geologic ages. The upper most
geologic type is the glacial till and outwash plains formed by the advance and
retreat of glaciers over a long period of time. The second layer of geologic
material is the Cretaceous bedrock. The lowest layer of geologic material is
the Precambrian, mostly igneous, basement bedrock. More detail about the
area bedrock geology can be obtained from the Steams County Geologic
Atlas, from which information used in this section was obtained.
Glacial till and outwash plain geology is commonly referred to as Quaternary
geology, named after the geologic period in which the glaciers advanced and
retreated. In the St. Joseph area, the glacial material ranges roughly from 25-
125 feet thick and is mostly comprised of areas of glacial till and sand
deposited by the St. Croix moraine of the Superior lobe and also outwash
sand and gravel from the Des Moines lobe (Figure 3).
The predominance of sands and gravel in the flatter regions of the St. Joseph
area is the result of glacial melt water outwash deposits from the glacial ice
margins. The Superior lobe sandy outwash deposits are present at depth in
the area and Des Moines lobe outwash sands are found at the surface. The
Des Moines lobe glacier did not advance as far as the St. Joseph area in
Stearns County, however the outwash sands did deposit over the already
existing Superior lobe sands and tills.
The steeper hill terrain on the south, west, and northwest sides of town are
mostly glacial till deposits from the Superior and Rainy lobes. The material
in the till deposits is a mix of rock, sand, silts and clays. In some areas these
materials will be found mixed together and in other areas there may be lenses
of sand or clay mixed in with general till deposits,
Bedrock geology in the area consists of undivided Cretaceous rocks that
overlie the Precambrian crystalline bedrock (Figure 4). The Cretaceous
bedrock, comprised mostly of soft shales, claystone, and silty fine sandstone,
once extended across most of the Steams County area and was eroded away
from a large part of the county during glacial periods, The remnants of the
Cretaceous rock are mostly in the eastern part of the county. In the study
area, the thickness of the Cretaceous bedrock is mostly between 100-150 feet
thick, but ranges from 50-200 feet thick.
The lowest layer of geologic material is the Precambrian crystalline bedrock.
The Precambrian rock underlies the Cretaceous layers and oruy subcrops in a
few areas within the study area. The crystalline bedrock is only partly
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defmed because of its depth; however, through drill records it has been found
to be mostly granites, with areas of schist (Little Falls fonnation) and gabbro.
2.2 Hydrogeology
Ground water is present in the different geologic units, with several areas
noted as having the capacity to produce enough useable quantity of water to
be called aquifers. These units are the quaternary glacial sand and gravel
water-table aquifers, the quaternary confined aquifers, the Cretaceous aquifer
and the Precambrian bedrock aquifer.
The quaternary water-table aquifer is composed of glacial outwash sands and
gravels. This aquifer is open to inflow from the land surface, with no
confining clay lenses above it. Figure 5 shows the generalized water table
map of the quaternary aquifer in feet above mean sea level. The Stearns
County Geologic atlas shows generalized aquifer yields on Plate 8 of 10. In
general, the water table elevation is found to be about 20 feet below the land
surface. The general groundwater flow is toward the Sauk and Mississippi
Rivers. Ground water in the area is generally of a calcium, magnesium, and
bicarbonate type, with wells drilled from 20 to 330 feet (averaging 85 feet)
deep.
The Cretaceous aquifer is of limited extent over Stearns County as a whole;
however, it is considered an important ground water source in the St. Joseph
area. The Stearns County Geologic Atlas shows that this geologic unit is up
to 200 feet thick in this area and thus could be an important ground water
resource.
The Precambrian bedrock also has some potential as an aquifer for the St.
Joseph area, Most of Steams County does not have this resource, but it is
present in the study area. Well borings have to be drilled quite deep in order
to have sufficient storage to achieve even 10 gallons per minute yield, and so
their use is limited mostly to domestic wells.
2.3 Soils
The main source of information for soils mapping and types in Minnesota is
the Natural Resource Conservation Service (NRCS) Soil Surveys. The Soil
Surveys were published across Minnesota by county; the Steams County Soil
Survey was published in 1985. The Soils Surveys show maps of the county
with the individual soil symbols and their boundaries for each of the soil
types. There are also tables of infonnation about the soil classifications and
characteristics.
These Soils maps and data are being updated and republished in a digital
fonnat. These new soils maps are called SSURGO soils data, and are
available in a GIS database (Arc View) format. The Steams County Soil and
Water Conservation District, Waite Park, Minnesota, has information on
obtaining soil survey information.
The NRCS has established four hydrologic soil groups based on their runoff
producing characteristics as described below:
.
.
Group A - High infiltration, low runoff potential
Group B - Moderate infiltration
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Storm Water Management Plan
St. Joseph, Minnesota
. Group C - Slow infiltration rate
. Group D - Very slow infiltration rate, high runoff potential
In general, Group A soils are mainly deep, well drained, and sandy or
gravelly soils, Group D soils may have a high percentage of clay or a clay
layer at or near the surface, have a permanent high water table, or are shallow
over nearly impervious bedrock.
The runoff potential of an area for engineering design is determined using the
soil's hydrologic soil group in combination with land slope, land use
classifications, vegetation of the area and rainfall intensity determined from
charts for the various design storms.
Soils within the S1. Joseph area include a broad range of soil types, however,
the sandy loam and loamy sand types predollÚnate. Figure 6 shows the
distribution of soils by USDA texture classification. Table 1 lists the soils
name, symbol, acres covered, hydrologic group, and USDA soils texture of
the different soil types within the study area. Table 2 lists the percentage of
area within each of the different USDA texture types and hydrologic soils
group.
Sandy loam and loamy sand textured soils have a high percentage of sand,
are well drained, and tend to have moderate to high infiltration capacity with
low runoff potential. Data on Table 1 shows that these soils are mostly in the
A or B hydrologic group.
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2003 Storm Water Management Plan 811112004
ST. JOSEPH, MN
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TABLE 1: STUDY AREA SOIL TYPES
SOIL TOTAL HYDROLOGIC USDA TEXTURElMAPPING
SYMBOL SOIL NAME ACRES GROUP GROUP SOIL GROUP
1016 Udorlhents, loamy 8.3 varied graded or filled material graded or filled material
Total acres graded or filled material: 8.3
133B Dalbo loam, 2 to 8 percent slopes 16.0 B loam loam
156A Fairhaven loam, 0 to 2 percent slopes 2.6 B loam loam
180A Gonvick loam, 1 to 2 percent slopes 1.7 B loam loam
38B Waukon loam, 2to 6 percent slopes 13.6 B loam loam
38C Waukon loam, 6to 12 percent slopes 2.3 B loam loam
413 Osakis loam 490.2 B loam loam
566 Regal loam 74.5 BID loam loam
Total acres loam: 601.0
454B Mahtomedi loamy coarse sand, 2 to 8 percent slop 252.9 A loamy sand loamy coarse sand
454C Mahtomedi loamy coarse sand, 8 to 15 percent slo 62.9 A loamy sand loamy coarse sand
454E Mahtomedi loamy coarse sand, 15 to 25 percent sl 21.0 A loamy sand loamy coarse sand
454F Mahtomedi loamy coarse sand, 25 to 40 percent sl 0.1 A loamy sand loamy coarse sand
181 Litchfield loamy sand 102.5 A loamy sand loamy sand
207B Nymore loamy sand, 2 to 8 percent slopes 3.7 A loamy sand loamy sand
207C Nymore loamy sand, 8 to 15 percent slopes 130.5 A loamy sand loamy sand
207E Nymore loamy sand, 15 to 25 percent slopes 51.6 A loamy sand loamy sand
260 Duelm loamy sand 96.1 A loamy sand loamy sand
611C Hawick loamy sand, 6 to 12 percent slopes 6.8 A loamy sand loamy sand
6110 Hawick loamy sand, 12 to 40 percent slopes 9.5 A loamy sand loamy sand
7A Hubbard loamy sand, 0 to 2 percent slopes 298.8 A loamy sand loamy sand
7B Hubbard loamy sand, 2 to 6 percent slopes 627.3 A loamy sand loamy sand
7C Hubbard loamy sand, 6 to 12 percent slopes 76.4 A loamy sand loamy sand
261 Isan loamy sand 9.9 NO loamy sand loamy sand
875B Estherville·Hawick complex, 2 to 6 percent slope 38.3 B loamy sand loamy sand
159B Anoka loamy sand, 2 to 8 percent slopes 53.4 B loamy sand loamy sand
179B Langola loamy sand, 1 to 4 percent slopes 14.2 B loamy sand loamy sand
453B DeMontreville loamy sand, 2 to 8 percent slopes 259.1 8 loamy sand loamy sand
453C DeMontreville loamy sand, 8 to 15 percent slopes 78.3 8 loamy sand loamy sand
1018 Udifluvents, frequenlly flooded 35.5 varied loamy sand sand to sandy loam
Total acres loamy sand: 2,229.0
1015 Psamments, sloping 16.0 A sand and gravel sand
1029 Pits, gravel 123.0 A sand and gravel sand and gravel
Total acres sand and gravel: 139.0
327A Dickman sandy loam, 0 to 2 percent slopes 580.7 A sandy loam sandy loam
327B Dickman sandy loam, 2 to 6 percent slopes 408.6 A sandy loam sandy loam
1843C Cushing·DeMontreville complex, 8 to 15 percent s 42.7 8 sandy loam sandy loam
1843E Cushing-DeMontreville complex, 15 to 25 percent 37.4 8 sandy loam sandy loam
1558 Chetek sandy loam, 1 to 6 percent slopes 40.5 B sandy loam sandy loam
1842F Cushing and Flak sandy loams, steep 1.7 B sandy loam sandy loam
204B Cushing sandy loam, 2 to 8 percent slopes 1,015.4 B sandy loam sandy loam
204C Cushing sandy loam, 8 to 15 percent slopes 255.5 B sandy loam sandy loam
204E Cushing sandy loam, 15 to 25 percent slopes 31.8 8 sandy loam sandy loam
2928 Alstad sandy loam, 1 to 4 percent slopes 323.6 B sandy loam sandy loam
41A Estherville sandy loam, 0 to 2 percent slopes 2,536.8 B sandy loam sandy loam
418 Estherville sandy loam, 2 to 6 percent slopes 907.5 8 sandy loam sandy loam
41C Estherville sandy loam, 6 to 12 percent slopes 30.7 B sandy loam sandy loam
465 Kalmarville sandy loam, frequently flooded 233.4 B sandy loam sandy loam
639A Ridgeporl sandy loam, 0 to 2 percent slopes 100.8 B sandy loam sandy loam
639B Ridgeporl sandy loam, 2 to 6 percent slopes 97.4 B sandy loam sandy loam
281 Darfur coarse sandy loam 349.4 BID sandy loam coarse sandy loam
183 Dassel sandy loam 556.6 810 sandy loam sandy loam
142 Nokay fine sandy loam 0.8 C sandy loam fine sandy loam
163B 8rainerd fine sandy loam, 1to 4 percent slopes 47.2 C sandy loam fine sandy loam
325 Prebish sandy loam, depressional 23.1 CID sandy loam sandy loam
Total acres sandy loam: 7,621.5
W Water 314.5 water water
Total acres water: 314.5
1825C Seelyeville muck, sloping 4.9 NO weiland soils wetland soils I muck
540 Seelyeville muck 65.3 NO weiland soils wetland soils I muck
543 Markey muck 420.3 NO wetland soils wetland soils I muck
544 Cathro muck 18.9 NO wetland soils wetland soils I muck
541 Rifle mucky peat 61.5 NO wetland soils wetland soils I muck peat
873 Prebish-Nokay complex 223.9 C/O wetland soils wetland soils /Ioam
1055 Histosols and Haplaquolls, ponded 186.5 0 wetland soils wetland soils I organics
Total acres wetland soils: 981.3
Total Area: 11,894,61
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Table 2
Summary of Soils Group
Summary By USDA Texture
USDA Texture
Filled Materials
Loam
Loamy Sand
Sand and Gravel
Sandy Loam
Wetland Soils
Water
Total:
Acres
8,3
601.0
2,229.0
139,0
7,621.5
981.2
314.6
11,894.6
Percentage
of Total
0.1%
5.1%
18.7%
1.2%
64,1%
8.2%
2.6%
100.0%
Summary By Hydrologic Soils Group
Hydrologic
Soil Group
A
ND
B
BID
C
CID
D
Varied
Water
Total:
Acres
2,868.6
580.8
6,624.9
980.5
48.1
246.9
186.4
43.8
314,6
11,895
Percentage of
Total
24.1%
4.9%
55.7%
8.2%
0.4%
2.1%
1.6%
0.4%
2.6%
100,0%
Soils with a dual hydrologic soils group classification, such as AJD, indicate
that where these soils are artificially drained, the first designated hydrologic
group should be used. However, in a natural, undrained condition, the second
less pervious group should be used. These soils may have a high percentage
of sand or other pervious soils, but they are often found in wetlands or areas
with high groundwater tables, so they are saturated and have low infiltration
capacities.
Soil characteristics are also considered when developing erosion control
plans. Special procedures for erosion and sediment control should be
incorporated into all construction projects. The Erosion Control Handbook
published by Minnesota Department of Transportation, 2002, includes
reconnnended management practices, The MPCA published a document
titled Protecting Water Quality in Urban Areas, Best Management Practices
for Dealing with Storm Water Runoff from Urban, Suburban and Developing
Areas of Minnesota, 2000, which may be used for reference. This manual can
be found on the Internet at www.pca.state.mn.usfwaterfpubsfsw-bmpmanual.
Precipitation
Climate within the St. Joseph area is described as a humid continental
climate with moderate precipitation, wide daily temperature variations, warm
humid sunnners and cold winters. The total average annual precipitation is
approximately 29 inches. The average annual snowfall is approximately 47
inches, which is equivalent to roughly 4.7 inches of water. Rainfall data for
the St. Joseph area is shown in Table 3.
2.4
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Table 3
Rainfall in St. Joseph Area
(inches)
Return 24-hour 12-hour 6-hour I 3-hour 2-hour I-hour 30 - 15 -
Frequency minute minute
1- year 2.2 1.8 1.6 1.3 1.2 1.0 0,8 0.6
2-year 2.6 2.2 1.9 1.6 1.5 1.2 0,9 0.7
5-year 3.4 2.8 2.4 2.0 1.8 1.5 1.2 0.9
10-year 4.0 3.2 2.8 2.4 2.1 1.7 1.4 1.0
25-year 4.6 3.9 3.3 2.8 2.6 2,1 1.6 1.2
50-year 5.2 4.4 3.8 3.2 2,9 2.4 1.9 1.4
100-year 5.8 5,0 4.3 3.7 3.3 2.7 2.1 1.5
2.5
The 24-hour rainfall for different rain events for the State of Minnesota is
shown in Appendix C, The table and figure represent climatological
information found in the D.S, Department of Commerce, Weather Bureau
Technical Paper No. TP-40.
The 24-hour duration, NRCS Type II rainfall distribution with average soil
moisture conditions (AMC-2) will be used for overall subwatershed planning
within the city of St. Joseph.
Lakes, Rivers, and Wetlands
St. Joseph has numerous lakes and wetlands within and around the City
limits. Some of these lakes and wetlands can be classified in the Public
Waters Inventory (PWI) based on the MNDNR standards discussed below.
Figure 7 shows the identified public waters and lakes within the study area.
Table 4 lists the lakes and wetlands and provides acreage and public water
identification numbers, St. Joseph has adopted Shoreland Management
Standards,
2.5.1
Lakes
There are seven lakes that lie near the City limits of St. Joseph: Lower
Watab, Watab, Rossier, Kraemer, Lake Sarah and two unnamed lakes, Table
4 shows the lakes for the study area. Figure 7 shows the lakes and ill
numbers.
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Table 4
St. Joseph Area lakes and Wetlands
Lake Name TRS MnDNR ID PWI Number Acreage
Lower Watab 125-29-35 73007100 71P 15,6
Watab 125-29-35 73007000 70P 88.4
Rossier 125-29-35 73007200 72P 30.1
Unnamed 125-29-34 73031300 313W 6.5
Kraemer 124-29-17 73006400 64P 187.0
Lake Sarah 124-29-16 73006200 62P ILl
Unnamed 124-29-16 73006300 63N 22.5
Wetland 125-29-34 499W
Wetland 125-29-33 314W
Wetland 124-29-1 560W
Wetland 124-29-1 561W
Table 4 Notes: TRS = Township, Range and Section
The MNDNR classifies lakes according to the following three types:
· Natural Environment Lakes Usually have less than 150 total acres, less
than 60 acres/mile of shoreline, and less than 3 dwellings/mile of
shoreline, They may have a shallow, swampy shoreline, and are less
than 15 feet deep.
· Recreational Development Lakes Usually have between 60 and 225
acres/mile of shoreline, between 3 and 25 dwellings/mile of shoreline,
and are more than 15 feet deep.
· General Development Lakes Usually have more than 225 acres of
water/mile of shoreline, 25 dwellings/mile of shoreline, and are more
than 15 feet deep.
Of the lakes in the study area, Kraemer and Watab have Recreational
Development classifications and Lower Watab, Rossier, Lake Sarah, and
73006300 have Natural Environment classifications.
The MPCA classifies lakes according to water use categories, Waters of the
state are classified based on suitability for domestic consumption, fisheries
and recreational use, industrial use, agricultural and wildlife use, aesthetic
enjoyment, navigation, and other categories. The explanation for this system
can be found in Minnesota Rules chapter 7050.
The lakes in the S1. Joseph area are classified, along with most of the rest of
the lakes in Steams County as: a) intennediate quality fisheries and aquatic
recreation, b) general industrial purposes, c) irrigation quality, d) livestock
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and wildlife without injurious effects, e) aesthetic enjoyment and navigation
and suitable for aesthetic enjoyment, and f) other non-specific uses.
2.5.2 Rivers
Figure 7 shows the river systems in the St. Joseph area. The Watab River and
its tributaries are in the north part of the area. The Watab River flows
northeastward, through Rossier and Watab Lakes, and discharges at the
Mississippi River in Sartell.
The Sauk River is in the south part of the area and flows northeastward to
discharge at the Mississippi River between Sartell and St. Cloud.
2,5.3 Wetlands
Figure 8 shows the wetlands within and around the City of St. Joseph that are
included in the National Wetlands Inventory (NWI). Table 5 provides a list
of the study area wetland types and classifications by section. The wetlands
listed in Table 5 are classified by the U.S. Fish and Wildlife Service Circular
39 system (1971). Table 6 provides the definitions for the Circular 39
classifications.
Another commonly used classification system is the Cowardin system, which
classifies wetlands according to ecology, location in the watershed, bottom
and vegetation types and water regime. An example of this classification
would be PEM (palustrine, Emergent). Definitions for the Cowardin
classifications can be found on the Minnesota DNR, legislative, and BWSR
websites.
The Minnesota wetlands law is outlined in Minnesota Rules chapter 8420,
the Wetland Conservation Act (WCA). These rules are promulgated and
enforced by BWSR. In Steams County, the County Environmental Services
Department is the local regulating authority (LGU) for wetlands r:egulations.
Whenever an area with potential wetlands will be impacted by construction,
earth disturbance or inundation, the project owner is responsible under WCA
rules to have the wetlands delineated and to complete a wetland permit for
review by the LGU.
Steams County is located in the area of the state with less than 50 percent of
pre-statehood wetland area remaining. This means that any wetland located
on non-agricultural land must be replaced at a ratio of at least two to one for
each area of drained or filled wetland,
Storm Water Management Plan
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Wetland
Type
1
Table 6
Wetland Classification
Definition
2
Seasonally flooded basin or flat. Well-drained much of growing
season.
Wet meadow. Usually without standing water but has water within a
few inches of surface,
Shallow marsh. Soil usually waterlogged early in growing season and
often contains up to 6 inches of water.
Deep marsh. Soil usually covered with 6 inches to 3 feet of water
during growing season. .
Shallow open water. Water usually less than 10 feet deep and fringed
by emergent vegetation.
Shrub swamp. Soil is usually waterlogged during the growing season
and is often covered with as much as 6 inches of water,
Wooded swamps. Soil is waterlogged at least to within a few inches
of the surface during the growing season and often covered with as
much as 1 foot of water,
Bogs. Soil is usually waterlogged.
3
4
5
6
7
8
90
Riverene systems.
In the study area Sections there are 492 wetlands with a total acreage of
1,728 acres. Type 3 wetlands are the majority of wetlands in the study area,
with 954 acres, or 54 percent of the total wetland acres in the area.
2.5.4 Public Waters
The Minnesota Department of Natural Resources (MNDNR) Public Waters
which lie within and around the City limits can be seen in Figure 7. The
MNDNR Public Waters comprise waterbasins and watercourses that meet
criteria set forth in Minnesota Statutes, Section 103G.005, subd. 15 and l5a.
Public waters wetlands include Type 3, 4, and 5 wetlands, as defined in U.S.
Fish and Wildlife Service Circular 39, 1971 edition, that are 10 acres or
greater in size in an unincorporated area or 2-1/2 acres or greater in an
incorporated area. Minnesota Statute Section 103G.005, subd, 17b defines
the Circular 39 wetland types. MNDNR Waters have county maps to show
the location of public water and public waters wetlands. These maps are
commonly called Public Waters Inventory (PWI) maps, There are also
county lists available in tabular form. The boundary of the wetlands and
waters is called the ordinary high water level (OHWL). This is the regulatory
boundary for MNDNR waters. Above the OHWL there is the Shoreland
Wetland Protection Zone.
For local government units with a shoreland management ordinance
approved under sections 103F.201 to l03F.221, the shoreland protection
zone is either:
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St. Joseph, Minnesota
A-ST JOE0315
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(i) 1000 feet from the OHWL of a waterbasin that is a public water
identified in the shoreland management ordinance or the shoreland area
provided in the shoreland management rules adopted under section
103F.211, whichever is less, or
(ii) 300 feet from the OHWL of a watercourse identified in the shore land
management ordinance or the shoreland area approved by the
commissioner as provided in the shore land management rules adopted
under section 103f.211, whichever is less.
Areas shown on the PWI maps indicate the presence of wetlands, but show
only the general location of wetlands, Site visits for delineation of wetland
boundaries are required for permitting, It should also be noted that some of
these wetlands may have been created as stormwater detention basins in
conjunction with urban development.
S1. Joseph has public waters within and around the City, The lakes and
wetlands provide an environmental habitat for fish and wildlife within the
City, These water bodies should be protected from degradation by pollution
or contamination from surface water or groundwater sources,
2.6 Biological Survey
For information about rare animals and unique areas within the S1. Joseph
study area, contact the Stearns County Environmental Services, You can also
refer to the Stearns County Biological Survey,
2.7 Land and Water Use
2,7.1 Land Use
Existing land use is shown on Figure 9, which shows land use as reported by
the Stearns County Assessors' office for the study area, Actual land use has
been found to vary for some parcels from the Stearns County data, Most of
the area inside the City limits is shown as residential, with a large area
classified as institutional for the St. Benedict College campus, and
commercial and industrial districts along the highways. Outside the City
limits, most of the area is currently classified as agricultural.
S1. Joseph has ten parks and also a playground located at Kennedy
Elementary School within its City limits. The City intends to maintain these
park areas, make necessary improvements to the park system, and continue to
expand the trail system to connect the neighborhoods to these parks and other
trails. The parks are a vital part of the St. Joseph community,
As the population of the S1. Joseph area continues to increase, planning is
underway for the development of new residential areas and annexation of
additional properties to the City, Figure 10 shows the S1. Joseph planned
orderly annexation agreement zones, The existing developed area lies just to
the south and north of CSAH 75, The planned annexation area will add about
4,700 acres (235 percent) to the existing 2,000-acre City, The City limits are
expected to extend further north, south, and east from their current
boundaries,
Figure 11 shows the planned future land use for the St. Joseph orderly
annexation area. The dominant share of land within St. Joseph is anticipated
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S1. Joseph, Minnesota
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to be residential with corridors and areas identified for commercial, industrial
and park uses.
Large developments often utilize a Planned Unit Development (PUD) zoning
approach. A PUD allows the City and developer to include different land use
types within one development plan. Land use types typically include single-
family residences, townhomes, apartments, park and open areas, and
sometimes a commercial area,
2.7.2 Water Quality and Water Use
Water Quality
Minnesota's rivers, streams, lakes, wetlands, and aquifers are a valuable
resource for the state. Not only do they provide natural beauty, they supply
the water necessary for aquatic life, recreation, industry and agriculture,
Every two years, MPCA is required under the Federal Clean Water Act,
section 303(d), to publish an updated list of streams and lakes that are not
meeting their designated uses because of excess pollutants. The Sauk River
sections through and downstream of St. Joseph are listed as impaired for
mercury, PCB and fecal coliform. Appendix D shows this part of the most
recent MPCA list (12/18/2003) for 303(d) impaired waters. These sites are
listed as having no US EP A approved plan for mediating the impairment.
Until there is an approved plan, no special runoff treatment measures are
required.
Also, Minnesota periodically assesses individual stream reaches, lakes,
wetlands, and aquifers as required by section 305(b), The 305(b) lists are
considered a first step to naming waters on the 303( d) list; the 305(b) list is
available on the MPCA website: www.pca.state.mn.us/water/index.html
The term TMDL (Total Maximum Daily Load) is used to define what is the
maximum concentration of any pollutant that can be in a water, and can still
be used for its designated uses, such as drinking water, fishing, swimming,
irrigation and industrial uses, The MPCA will be approving TMDL studies
for different water bodies and watersheds as funding is available to conduct
them, Once the approved TMDL plans are in place, local jurisdictions will be
required to address the water quality concerns that pertain to affected
waterbodies.
Water Appropriation Permits
There is only one water appropriation permit issued by the MNDNR in the
area to the City of St. Joseph. Water appropriation permits are issued to the
permittees who pump greater than 10,000 gallons per day or over one million
gallons of water per year. The permit information can be seen below in Tbl 7.
Table 7
Water Appropriation Permit
Permit No.
Owner
Location Pumping Limits (mgy)
893101 City of St. Joseph Section 9
mgy ::: million gallons per year
150
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Storm Water Management Plan
St. Joseph, Minnesota
Groundwater Sensitivity to Pollution Data
The MNDNR, Division of Water's, prepared a map showing areas of the
county that have greater or less potential for aquifer contamination (Stearns
County Geologic Atlas, Plate 10/10). The map shows the county with
sensitivity to pollution rating levels of very high, high, moderate, and low.
These levels were obtained by combining three geologic and hydrogeologic
factors: depth to water table, surficial geology, and subsurface permeability.
A composite map of these factors was created utilizing a geographic
information system (GIS) for the County Geologic Atlas, Figure 12 shows
the portion of this analysis for St. Joseph and the surrounding area,
Most of the area has a medium to very high sensitivity to ground water.
Table 8 shows the distribution of this rating in the study area. The ratings
with the largest areas are 'medium sensitivity', with approximately 18.2
percent of land area in the study area, 'high sensitivity' - 23.7 percent, and
'very high sensitivity' - 55.6 percent.
Table 8
Ground Water Sensitivity to Pollution
Sensitivity
Rating Description Acreage % of Total Land
L Low 83.9 1
M Medium 2,181.0 18
H High 2,841.6 24
VH Very High 6,675.7 56
NR Not Rated 211.8 2
Well-Head Protection
There is currently no well-head protection plan in place in the City of St.
Joseph. A new City well is being planned, and it is anticipated that the well-
head protection plan will be started in late 2004 or 2005. The Minnesota
Department of Health currently has a Source Water Assessment Report for a
community to rely on until they have their own well-head protection plan.
This report can be found at the following site for the study area:
http://156,98.150,16/swa/pdwgetpws.cfm
Water-Based Recreation Areas
Kraemer and Watab Lakes are listed as Recreational Development lakes by
the MNDNR. Kraemer Lake has a water depth of approximately 30 feet, with
public water access located on the east shore owned by the St. Joseph Rod
and Gun Club. The Sauk River can also be used for recreational activities
such as fishing and canoeing.
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Storm Water Management Plan
St. Joseph, Minnesota
Identified Pollutant Sources
Two pollutant sources within the study area are identified by the MPCA. The
sources are listed below in Table 9, All pollutant source sites have been
identified and are in various stages of soil and groundwater remediation.
Table 9
Pollutant Sources
Site ill
Site Name
Location
MNPTOOOO2920
Joseph Street
DBL Labs
MNODIOOOl198
Saint Joseph
Dump Site
1/4 mile NW of intersection of
Highway 2 and CSAH 75
The MPCA also maintains lists of the generators of hazardous waste, above
ground and under ground storage tanks, and leaking underground storage
tanks. A list of the generators of hazardous waste in the study area is
included in Appendix E. There are numerous registered above-ground and
under-ground tank sites in the area. Some of these sites and some non-
registered sites have had leaking under-ground storage tanks. This
information can be found on the MPCA website.
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