BLACKFEET NATION
EARL OLD PERSON. CHAIRMAN
AL POnS. VICE CHAIRMAN
LEE Wll SON. SECRETARY
ELAINE GUARD!PEE. TREASURER
EXECUTIVE COMMITTEE
P.O. BOX 850
BROWNING, MONTANA 59417
(406) 338-7179
FAX 338-7530
BLACKFEET TRIBAL BUSINESS COUNCIL
EARL OLD PERSON
al pons
LEE WILSON
JOE MCKAY
DONMAGEE
CYNTHIA KIPP
MAIUENE WALTER
GEORGE RUNNING WOLF
FRANKLIN COMES AT NIGHT
US Environmental Protection Agency
Region VIII
Denver, Colorado
Clean Lakes Coordinator
David Rathke, PhD:
Enclosed is a draft of the Final Report for the (314) Clean Lakes Program. A copy of this report
has been sent to Lee Roberts for his review. Our office apologies for the extended delay of this
document, but gathering of data, organizing it, and incorporating it into the final product took
longer than we anticipated.
We hope this report will confer to your office the direction in which the Blackfeet Environmental
Office is pursing water Quality. We are working very hard to complete tasks and objectives
which were already in place before we arrived at this job.
Our office would appreciate any suggestions or comments regarding this report. If you have any
questions, please contact our office at (406) 338-7421. Thank You
Environmental Scientist,
Pat F. Calf Looking
cc: Crono file

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* 2-6 H
Final Report
(314) JCLEAN LAKES PROGRAM OF
THE BLACKFEET INDIAN RESERVATION
Prepared! for s
ENVIRONMENTAL PROTECTION AGENCY
REGION V111
Eetleral BuiMing, rim. 28<5>
Soutlk park, Drawer
Helena, Mt„ 596>26>~0096>
ATTENTION;
Lee Roberts
Davinl Ratltake
SUBMITTED BY;
Tli
"" Me Olac
Wayne Smitli, Administrative Director
Pat F. Calf Looking, Environmental Scientist
(Jiera U Wagner , E mviron mental Scientist
Henry Butterfly, Water Teclicican
U-S, EPA Region 8 Libra
mm loiorm

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CONTENTS
PARTI DRAINAGE BASIN DESCRIPTIONS
Introduction 1
Location of Lakes 2
Drainage Basin Size 3
Annual Runoff in Basins 3
PARTS LAKE DESCRIPTIONS
St. Mary Drainage Basin
Duck Lake 4
Flat Top Lake 10
Pike Lake 16
Sherburne Reservoir 22
St. Marys Lake 28
Milk River Drainage Basin
Goose Lake 34
Horse Lake 40
Cut.Bank Drainage Basin
Guardipee Lake 46
Hidden Lake 52
Hope Lake 57
Kipp Lake 63
Mission Lake 69
No Chief Lake 75
Railroad Lake 81
Sharp Lake 87
Whiskey John Lake 93
Two Medicine Drainage Basin
Alkali (South) Lake 98
Cooper Lake 104
Dog Gun Lake 110
Four Horns Lake 116
Magee Lake 122
Mittens Lake 128
Swift Reservoir 134
Twins, North Lake 140
Twins, South Lake 146
Two Medicine Lake 152

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INTRODUCTION:
Characterization of lakes
on the Blackfeet Reservation
The Blackfeet Reservation consists of a diversity of lakes.
Enclosed in the 1.5 million acres of the Reservation boundaries
are incredible mountainous lakes, magnificent foothill and
grassland lakes, and numerous prairie pothole water bodies.
Also, various reservoirs originate on the western side of the
Blackfeet Reservation.
The multitude of lakes on the Reservation support a variety
of uses of which include the following: sanctuary for waterfowl,
bolster first-class fishing, and provide water for agricultural,
animal, and human applications. Also, ecosystems depend heavily
on the water quality of these Reservation lakes.
There are four major drainage basins residing on the
Blackfeet Reservation. They are the Cut Bank, Milk River, St.
Marys, and the Two Medicine drainage basins. The Milk River and
St. Marys basins empty into southern Alberta in Canada. The Cut
Bank and Two Medicine basins discharge into the Missouri River
and eventually into the Mississippi River. The drainage basins
begin at the Continental Divide.
The water quality of the lakes listed in this report will be
determined and then an preliminary assessment will be completed.
Chemical, biological, and physical characteristics will be the
principal factors taken into accout during this assessment
process, but other contributing elements will also be considered.
They include precipation, run off, erosion, dust, atmospheric
gases, underground water, etc.
This Clean Lakes Report is intended to inform the public and
EPA about the lakes on the Blackfeet Reservation with a primary
focus on the water quality of these lakes.
1

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PAGE NOT
AVAILABLE
DIGITALLY

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SIZE OF DRAINAGE BASINS
Basin
1.	St. Marys
2.	Milk River
3.	Two Medicine
4.	Cut Bank
Area Size
214 Square Miles
507 Square Miles
670 Square Miles
1,008 Square Miles
MEASURED ANNUAL RUNOFF
IN DRAINAGE BASINS
Basin
1.	St. Marys
2.	Milk River
3.	Two Medicine
4.	Cut Bank
1991 (acres-ft.)
592,700	measured
23,331	measured
679,100	measured
179,000	measured
1992 (acres-ft.)
279,000 measured
no data available
250,770 estimated
66,930 measured
3

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Sf. M^arys
Drainage B asin

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Duck Lake
Duck Lake is located in the St. Marys drainage basin, and is
the second largest lake on the Blackfeet Reservation. It is
situated a mile east of Babb, Montana and forty miles north of
Browning, Montana on BIA Highway 464. Also, Canada is perched
ten miles to the north of it. Duck Lake runs in an east-westerly
direction, and is solidified in the foothills of the Rocky
Mountain range.
There are two types of lands encompassing the shoreline of
Duck Lake. Fee land embraces all of the northern, eastern, and
western shores. Fee also can be found on three quarters of the
southern shore. This is where most of the colonizing has taken
place in the form of cabins, trailer homes, and other dwellings.
Tribal land is focused on the remainder of the lake where a
store, boat dock, and campsite are used as revenue for the tribal
budget.
Duck Lake supports a healthy fishery with seven species
currently abiding in its waters. Canadians and Tribal members
take full advantage of the opportunities which Duck Lake has to
offer them. Fishing, boating, swimming, wa'ter skiing, camping,
and picnicking are enjoyed by all.
Duck lake acts as a landlord to many water fowl species in
the summer months and a rest stop for migrating birds in the
spring and autumn months.
Drainage Basin Characteristics
Duck Lake has no defined tributaries flowing into it. It is
charged by ground water and run off. Duck Lake comprises part of
the St. Marys watershed, and is located in the eastern part of
it. Any excess water in Duck leaves via a culvert on the west
end of the lake and drains into the St. Marys River.
Duck Lake coincides in two distinct ecoregions one being the
Northern Rockies and the other being the Montana Valley and
Foothill Prairies. The riparian soils which surround this lake
include cobbly, gravelly, stony, and light clay loams. The
dominant vegetation which exist in these soils are the bearded
wheatgrass, rough fescue, and the blue bunch wheatgrass.
Duck Lake is used primarily for recreational purposes, but
stock also utilized Duck for watering on the east end. This
practice may be closed off in the near future. To the west, the
Rocky Mountains protrude into the sky. To the north, ranching is
the main industry in this basin.
4

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Lake Basin Characteristics
Duck Lake has considerable magnitude with a surface area of
1,449.40 acres and shoreline length of 52,662 feet. We measured
the middle of the lake twice in 1993 and found the deepest point
to be sixty-eight feet. This point is located directly north of
the tribal store and boat dock in the middle of the lake. The
timber stands, which were once abundant on the south west shores,
are now replaced with residential structures. The rest of the
Duck Lake shore line is covered with grassy type vegetation.
Duck Lake has an elevation of 5,021 feet with water levels
varying from year to year due to ground water and run off
contributions. There has been a serious lowering of the water
level over the past decade by several feet.
Water Quality
Duck Lake was monitored in 1974-75 and was entered into the
Blackfeet Tribal Water Quality Management Plan of 1981. Also,
the Blackfeet Environmental Office monitored this lake in 1993
under sec. 314 of the Clean Water Act.
Because of the relatively high calcium and magnesium levels
Table 3), Duck Lake's water is considered to be hard. Alkalinity
is also elevated indicating the lakes ability to neutralize
strong acids.
At this time, Duck Lake would be classified as a mesotrophic
water body because of the results obtained in the last two years.
Our data shows a moderate amount of nutrients in the fall months
with chlorophyll a shifting when changes in total phosphorus and
nitrogen levels occur. The results in October of 1993 show an
intermediate quantity of Phosphates and Nitrates indicating an
algae growth in the lake.
Biological Characteristics
Fish:
Duck Lake currently houses seven species of fish. The fish
fauna are comprised of the following: rainbow trout, brown trout,
brook trout, lake chub, fathead minnow, white sucker, and
Bonneville cutthroat trout.
5

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Table 1. Characteristics of Duck Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Cobbly, Gravelly, Stony, and
Light Clay Loams. (Loam).
Unavailable
Unavailable
Northern Rockies, Montana
Valley and Foothill Prairies
Aspen: Bearded Wheatgrass,
Rough Fescue, Bluebunch
Wheatgrass
Unknown
Unknown
6

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Table 2. Characteristics of Duck Lake.
elevation (ft.)
5,021.00
surface area (acres)
1,449.40
volume (acre-ft.)
Unknown
maximum depth (ft.)
68.0
mean depth (ft.)
Unknown
shoreline length (ft.)
52,662.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-24"
mean residence time (yr.)
Not available
control structure
None
7

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Table 3. Major ions and related water quality variables for Duck
Lake. Average concentrations in mg/L; pH in pH units. Samples
were collected from euphotic zone on 28 October 1992, and twice
in 1993 on 4 August & 20 October. There were four grab samples
obtained at each visit.

1992
Mean
1993
Mean
pH (range)
9.00
8.89
alkalinity (mg/L CaCo3)
	
434.50
conductivity (umhos/cm)
443
685.00
turbidity (NTU)
3.20
1.26
dissolved oxygen
	
7.40
total suspended solids
3.44
1.77
Ca
25.82
24.39
Mg
73.97
76.06
K
8.75
8.83
Na
27.13
28.09
CI
3.39
3.31
S04
3.39
4.34
8

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Duck
Lake. Average concentrations in ug/L. Samples were collected
from the euphotic zone once on 28 Oct. 1992, and twice in 1993 on
4 August & 20 October. There were four grab samples obtained at
each visit.

1992
1993

Mean
Mean
total phosphorus
20.04
18.48
NH3-N
<1.80
13.88
N02/3
<2.80
5.09
chlorophyll a
6.34
1.61
secchi depth (ft)
8'
11'6"
9

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Flat Top Lake
Flat Top Lake is very hard to find and access. A four by
four vehicle would be needed to get to this lake. It is located
east of Flat Top Mountain, or a half mile west of St. Marys lake.
Babb lies in a round about way four miles to the north on US
Highway 89, and St. Marys community is three miles to the south
on the same highway.
This lake received its name from Flat Top Mountain. It is
not open to the public. The land encirling Flat Top Lake is in
trust status. There are no activities linked to Flat Top Lake
although it is regularly planted with trout by the Blackfeet Fish
and Game Department. Wildlife and forest abound in this area.
Drainage Basin Characteristics
Flat Top Lake sits close to the south west boundary of the
St. Marys drainage basin. It is the smallest lake in this basin.
Flat Top is charged by run off and ground water. There is no
visible outlet.
The Northern Rockies Ecoregion is the home to this lake.
Aspen, Lodgepole pine, and Douglas fir make up the vegetation
around the lake with loam type soils supporting them.
Most of the drainage basin is located north of Flat Top Lake
with mountains occupying the northwest side and prairies the
northeast portion.
Lake Basin Characteristics
The depth of this lake could not be measured because of
access problems with boat. Flat top is a small lake with a
surface area of 21.70 acres and a shoreline length of 4,459 feet.
Timber stands surround the lake with one road leading into it on
the west side.
Flat Top has an elevation of 5,658. This is one of the
higher lakes on the Blackfeet Reservation. Run off is the
biggest contributor to the volume of water.
10

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Water Quality
In 1965, some monitoring of Flat Top Lake did occur with the
data being entered into the Blackfeet Tribes Water Quality
Management Plan. The testing of its waters was resumed by the
Blackfeet Environmental Program in 1993 under Sec. 314 of the
Clean Water Act.
Flat Top Lake is a well buffered, freshwater lake. All
physical and chemical parameters look excellent (Table 3). The
water has a low hardness as predicted by calcium and magnesium
levels.
The total phosphorus content is extremely low with the
nitrogen levels even smaller. Also, the chlorophyll a
concentrations are almost non-existent. Put all three factors
above together, and this would add up to a oligotrophic lake.
Biological Characteristics
Fish:
Flat Top Lake contains Yellowstone Cutthroat Trout.
11

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Table 1. Characteristics of Flat Top Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Gravelly, Stony, and Cobbly
Clay Loams.
Unavailable
Unavailable
Northern Rockies
Douglas Fir, Englemann
Spruce, Lodgepole Pine.
Unknown
Unknown
12

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Table 2. Characteristics of Flat Top Lake.
elevation (ft.)
5,658.00
surface area (acres)
21.70
volume (acre-ft.)
Unknown
maximum depth (ft.)
Unknown
mean depth (ft.)
Unknown
shoreline length (ft.)
4,459.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
20" +
mean residence time (yr.)
Not available
control structure
None
13

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Table 3. Major ions and related water quality variables for Flat
Top Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 31 August 1993.
1992
1993
Mean
Mean
pH (range) 	
8.40
alkalinity (mg/L CaCo3) 	
147.40
conductivity (umhos/cm) 	
220.00
turbidity (NTU) 	
0.62
dissolved oxygen 	
6.60
total suspended solids 	
0.78
Ca 	
28.95
Mg 	
21.14
K 	
0.59
Na 	
31.98
CI 	
0.38
S04 	
2.33
14

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Flat
Top Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 31 August 1993.
TW2	1993
		Mean	Mean
total phosphorus			14.56
NH3-N			< 5
N02/3			< 2
chlorophyll a			0.79
secchi depth (ft)				
15

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Pike Lake
Pike Lake sits on the northern most reaches of the Blackfeet
Reservation. To reach Pike Lake, a traveler would have to take
US Highway 89 north of Babb for six miles, and then turn west on
a dirt road for four miles. Pike lies on the Blackfeet
Reservation boundary and the Canada line. Pike is set just below
the Rocky Mountains on its front range.
Pike Lake is surrounded by tribal land. There are a couple
of picnic sites on the east side of this lake. A loan
residential structure sits on a hill about a half of mile to the
south of the lake.
The name Pike Lake comes from the Pike fish that were
introduced there many years ago. Canadians as well as Americans
take advantage of the pike in this lake.
Wildlife and domestic animals utilize Pike Lake as a water
source. Waterfowl also can be seen resting on this cool pristine
mountain lake.
Drainage Basin Characteristics
Pike Lake rests on the northern most region of the St. Marys
drainage basin. Run off and ground water contribute to the
volume of water in this lake. A tributary outlet leaves Pike
Lake on the western side with the water flowing into Otatso
Creek. The water eventually ends up in the St. Marys River.
The Northern Rockies Ecoregion is where Pike Lake is located
at. The most persistent vegetation in this area is the bearded
wheatgrass, rough fescue, and the bluebunch wheatgrass. The
larger vegetation consist of the Aspen. The soils are cobbly,
gravelly, stony, sandy, and light clay loams.
The drainage basin has mountains to the west, prairies to
the east, and agricultural practices intensifying to the north.
Babb and St. Marys are the two towns located in this drainage
basin.
Lake Basin Characteristics
This is a fairly deep mountainous lake with 25 feet being
the deep point measured in 1993. Pike has a shoreline
measurement of 12,435 feet and a surface area of 102.40 acres.
It is nestled in a symmetrical valley of Aspens, willows, and
pines.
The USGS surveyed Pike Lake at 4,519 feet. Precipation is
the biggest donator to Pikes volume of water.
16

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Water Quality
The Water Quality Management Plan of the Blackfeet Tribe has
documentation that Pike was monitored in 1966. The water quality
of Pike was monitored more indepth by the Blackfeet Environmental
Office in 1993.
Pike Lake has excellent water quality. Pike is a well
buffered, fresh water lake. The water is moderately hard. The
main ions are calcium and magnesium (Table 3).
Total phosphorus and ammonia concentrations are reasonably
low, and this coupled with the almost non-existent chlorophyll a
levels would place Pike Lake under the oligotrophic bracket.
Other evidence supporting this assessment would be the clear
water and high secchi dish reading.
Biological Characteristics
Fish:
Pike Lake contains the Northern Pike species. There is no
other data available.
17

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Table 1. Characteristics of Pike Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Cobbly, Gravelly, Stony,
Sandy, and Light Clay Loams
Unavailable
Unavailable
Northern Rockies
Aspen, Bearded Wheatgrass,
Rough Fescue, Bluebunch
Wheatgrass
Unknown
Unknown
18

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Table 2. Characteristics of Pike Lake.
elevation (ft.)
4,519.00
surface area (acres)
102.40
volume (acre-ft.)
Unknown
maximum depth (ft.)
25.0
mean depth (ft.)
Unknown
shoreline length (ft.)
12,435.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-24"
mean residence time (yr.)
Not available
control structure
None
19

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Table 3. Major ions and related water quality variables for Pike
Lake. Average concentrations in mg/L; pH in pH units. A sample
was collected from euphotic zone on 26 August 1993.
1992	T993
	Mean	Mean	
pH (range)			8.38
alkalinity (mg/L CaCo3)			211.20
conductivity (umhos/cm)			417.00
turbidity (NTU)			0.79
dissolved oxygen			7.00
total suspended solids			0.78
Ca			42.18
Mg			26.59
K			1.18
Na			13.39
CI			1.27
S04			3.25
20

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Pike
Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 26 August 1993.
1992	1993
	Mean	Mean
total phosphorus			24.12
NH3-N			24.24
N02/3			2.90
chlorophyll a			0.79
secchi depth (ft)			16'7"
21

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Sherburne Reservoir
Sherburne Reservoir is located four miles west of Babb,
Montana on a paved road. The border of Canada lies fourteen
miles to the north east on US Highway 89. This magnificent lake
is etched into the Rocky Mountains in an east-westerly
orientation.
Most of Sherburne Reservoir resides in Glacier National
Park. Only the eastern tip of this lake is on tribal land which
also includes the control structure (dam). At the east end of
the reservoir, the famous Many Glacier Chalet can be found.
Sherburne Reservoir is used primarily by tourists in the
summer months. A boat dock is established at Many Glaciers which
accommodates rental of boats.
Drainage Basin Characteristics
Sherburne Reservoir is situated in the St. Marys drainage
basin on the extreme west side. Sherburne is charged by several
intermitted streams, run off, springs, and two tributaries.
Appekunny and Windy creeks enter Sherburne from the west side.
Water is released on the east side of the lake through Sherburne
Dam.
The Northern Rockies Ecoregion is the site of Sherburne
Reservoir. The timber stands surrounding this reservoir include
the Lodgepole pine, Englemann spruce, Douglas fir, Alpine fir,
and the Aspen. The soil makeup includes the cobbly, gravelly ,
stony, and cobbly clay loams.
The drainage basin is made up of mountains to the west and
foothill and prairies to the east.
Lake Basin Characteristics
Sherburne is a man made Reservoir which was once the
Swiftcurrent Creek basin. This reservoir is a semi-deep lake
with 44 feet being the inmost point. The surface area is
1,392.41 acres of which only 50.6 acres are located in the
Blackfeet Reservation boundaries. Sherburne has a perimeter of
6,954 feet with forest and a paved road paralleling the north
side and forest & mountain covering the south side.
The elevation, of is Sherburne Reservoir, is listed at 4,788
feet. The latest data has Sherburne storing 42,733 acre feet of
water in 1990 with 64,793 being the storage capacity of this
reservoir. The Specifications on this reservoir are noted on
(Table 2.).
Water volume and levels are determined mostly by the amount
of water released by Bureau of Reclamation. This agency is also
responsible for up keep of dam. Sherburne's water is used for
irrigational purposes with the Fort Belnap Indian Reservation
getting the majority of water via the Milk River.
22

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Hater Quality
Water quality was monitored in 1980 for a couple of
constituents. The ensuing results were placed in the Water
Quality Management Plan of the Blackfeet Nation. Water quality
was monitored more intensely in 1993 by the Blackfeet
Environmental Office.
Sherburne Reservoir is a freshwater lake because of low
concentrations of total suspended solids and salts. The amount
of calcium and magnesium tends to reveal the lakes relatively low
hardness.
The low concentrations of total phosphorus, nitrogen
compounds, and chlorophyll a definitely labels Sherburne as an
oligotrophic lake, but additional testing is needed to prove
analysis.
Biological Characteristics
No data available at this time.
23

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Table 1. Characteristics of Sherburne Reservoir drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Cobbly, Gravelly, Stony, and
Cobbly Clay Loams.
Unavailable
Unavailable
Northern Rockies
Alpine Fir, Aspen, Douglas
Fir, Englemann Spruce,
Lodgepole Pine.
Unknown
Unknown
24

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Table 2. Characteristics of Sherburne Reservoir.
elevation (ft.)
surface area (acres)
storage capacity (acre-ft.)
storage in 1990 (acre-ft.)
maximum depth (ft.)
mean depth (ft.)
shoreline length (ft.)
contol structures
dam height (ft.)
dam crest length (ft.)
overflow spillway crest
elevation (ft.)
mean annual lake evaporation (in.)
mean annual precipation (in.)
mean residence time (yr.)
Unknown
1,392.41 of which 50.6 acres
are on the Reservation.
64,793.00
42,733.00
44.0
Unknown
6,954.00
compacted earthfill with
concrete base slab
108.5
1,200.00
4,788.00
Unknown
20" +
Not available
25

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Table 3. Major ions and related water quality variables for
Sherburne Reservoir. Average concentrations in mg/L; pH in pH
units. A sample was collected from euphotic zone on 30 September
1993.
1992
1993
Mean
Mean
pH (range) 	
8.33
alkalinity (mg/L CaCo3) 	
61.60
conductivity (umhos/cm) 	
115.00
turbidity (NTU) 	
1.55
dissolved oxygen 	
8.40
total suspended solids 	
1.0
Ca 	
16.54
Mg 	
6.02
K 	
0.26
Na 	
0.80
CI 	
0.25
S04 	
3.49
26

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Table 4. Nutrient, chlorophyll a and Secchi depth data for
Sherburne Reservoir. Average concentrations in ug/L. A sample
was collected from the euphotic zone on 30 September 1993.
1992	1993
	Mean	Mean
total phosphorus			8.68
NH3-N			13.71
N02/3			4.41
chlorophyll a			1.74
secchi depth (ft)			11'10"
27

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St. Marys Lake
Lower St. Marys Lake is the largest and most utilized water
body on the Reservation. It lies on the northwestern fringe of
the Blackfeet Nation. St. Marys Lake is located a mile north of
the town of St. Marys and two miles south of Babb, Montana. The
lake is in a beautiful setting with the spectacular Rocky
Mountains west of it and rolling plains to the east.
The lakeshore is subdivided into lots which the Blackfeet
Tribal Council leases out. There are numerous dwellings which
surround this lake with the populace being represented on the
western shores. There is also a K.O.A. camp ground nestled on
the south west end of the lake which provides the following
services: fishing permits, camp sites and showers, store, etc.
St. Marys lake is most renowned for its fisheries. There
are many species of fish residing in this particular lake. The
most prominent being the lake and mountain whitefish. Also,
contained in this lake are the bull trout and westslope cutthroat
trout which are currently being considered for the endangered
species list. St. Marys Lake also supports many recreational
activities such as swimming, boating, water skiing, etc.
Another positive resource associated with St. Marys Lake are
the multitude of wildlife inhabiting its surrounding. The
grizzly bear, moose, and elk are a few of the big game which
utilize this lake as part of their livelihood.
Drainage Basin Characteristics
The drainage basin, which St. Marys Lake is situated in, is
the smallest basin on the Blackfeet Reservation, but has the
second highest acre-ft of water leaving the reservation. The
natural drainage has been altered by construction of a canal
diverting water out of St. Mary River about a mile below the
lake. The diverted water flows into the Milk River and
eventually Canada. St. Marys Lake is charged by run off, ground
water, and intermittent streams which are spring fed. The major
inflow into the lake comes from five major tributaries. St.
Marys River, Divide Creek, and Wild Creek enter the Lake from the
south. Swiftcurrent and Boulder Creeks charge St. Marys Lake
from the north end.
St. Marys Lake lies within the Northern Rockies Ecoregion.
The watershed consists of the Rockies to the west and is
characterized by mountainous valleys throughout. The soils are
comprised of cobbly, gravelly, and stony loams. The dominant
vegetation on these soils include Lodgepole pine, Douglas fir,
Englemann Spruce, and Aspen.
The drainage basin is covered by forest to the west and
rolling hills to the north with St. Marys Lake located in the
southwestern portion. There are a couple of towns concentrated
in this drainage basin of which was mentioned earlier.
28

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Lake Basin Characteristics
St. Marys Lake is a large, deep, mountainous lake with a
surface area of 2,187.40 acres. The deepest point was 64 feet,
which we measured in 1993, and is located across from an island
at midpoint of the lake. The shoreline is very long with dense
timber on the western side, a sandy delta on the north side, and
grassy/timber type vegetation on the eastern side. The length of
the shoreline was measured at 86,478 feet with it being owned by
the Blackfeet Tribe.
The elevation of St. Marys Lake was measured at 4,471 feet
according to the topographical map put out by the USGS
department. The water levels fluctuate from year to year. There
are multiple factors involved in the varying levels of water
during the year, but the dewatering of Sherburne Lake to the west
causes the most immediate change.
Water Quality
The water quality of St. Marys Lake was monitored in 1975
and entered into the 1981 Water Quality Management Plan (208) .
Also, the Blackfeet Environmental Office in 1993 monitored this
lake under the Clean Lakes Program.
St. Marys is a freshwater lake with concentrations of total
suspended solids and alkalinity lower than most lakes on the
reservation.
Because the levels of chlorophyll a and total phosphorus are
very low, the water transparency is quite clear. The low
concentrations of chlorophyll a is a good indicator that algal
biomass is low. Thus St. Marys Lake is more than likely to be
oligotrophic, but further monitoring is needed to confirm this
assessment.
Biological Characteristics
Fish:
Seventeen species of fish have been identified in the waters
of St. Marys Lake. They include the bull trout, westslope
cutthroat trout, lake trout, brook trout, rainbow trout, lake
whitefish, mountain whitefish, northern pike, longnose dace, lake
chub, pearl dace, longnose sucker, white sucker, trout perch,
burbot, spoonhead sculpin, and the shorthead sculpin. The
rainbow trout and a few other species of fish are stocked
annually. Commercial fishing is a big enterprise on this lake.
29

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Table 1. Characteristics of St. Marys Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Cobbly, Gravelly, Stony, and
Light Clay Loams. (Loam).
Unavailable
Unavailable
Northern Rockies
Aspen, Englemann Spruce,
Douglas Fir, Lodgepole Pine
Unknown
Unknown
30

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Table 2. Characteristics of St. Marys Lake.
elevation (ft.)
4,471.00
surface area (acres)
2,187.40
volume (acre-ft.)
Unknown
maximum depth (ft.)
64.0
mean depth (ft.)
Unknown
shoreline length (ft.)
86,478.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-24"
mean residence time (yr.)
Not available
control structure
None
31

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Table 3. Major ions and related water quality variables for St.
Marys Lake. Average concentrations in mg/L; pH in pH units.
Samples were collected from euphotic zone on 16 October 1992, and
twice in 1993 on 5 August & 21 October. There were four grab
samples taken at each visit.

1992
Mean
1993
Mean
pH (range)
8.04
7.92
alkalinity (mg/L CaCo3)
	
72.60
conductivity (umhos/cm)
	
125.50
turbidity (NTU)
1.33
0.67
dissolved oxygen
6.70
CD
Cn
CO
total suspended solids
2.16
0.5
Ca
24.89
23.11
Mg
6.34
6.09
K
0.30
0.25
Na
0.66
0.77
CI
0.19
5.67
S04
0.19
4 .03
32

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Table 4. Nutrient, chlorophyll a and Secchi depth data for St.
Marys Lake. Average concentrations in ug/L. Samples were
collected from the euphotic zone once on 16 Oct. 1992, and twice
in 1993 on 5 August & 21 October. There were four grab
samples taken at each visit.

1992
1993

Mean
Mean
total phosphorus
7.49
6.01
NH3-N
7.91
5.56
N02/3
37.81
43.98
chlorophyll a
E0.00
.159
secchi depth (ft)
none
2 6 ' 6 "
33

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Milk Ri
.ver
Drainage Basin

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Goose Lake
Goose is a medium sized lake which is situated a mile north
of Duck Lake and seven miles south of the Canadian border. A
four wheel vehicle is needed to get to this lake. The terrain is
very rough and hard to access. A trail north of Duck Lake will
get a visitor to Goose Lake. The shoreline is in fee status with
the lake owned and maintained by the Blackfeet Tribe.
Goose Lake is mainly utilized as a place for fishing. This
lake is one of a few which have brook trout residing in them.
The Blackfeet Fish and Game actively stock this lake.
Drainage Basin Characteristics
Goose Lake sits on the northwest fringes of the Milk River
drainage basin. It is only one of two lakes in this basin.
There are no inlets or outlets to this lake. Water volume is
depends on run off and ground water.
Goose Lake is situated in two ecoregions. They are the
Northern Rockies Ecoregion and the Montana Valley and Foothill
Prairies Ecoregion. Under normal conditions, bearded wheatgrass,
rough fescue, and bluebunch wheatgrass are the types of
vegetation which would thrive in area. These grasses are
supported by cobbly, gravelly, stony, and light clay loams.
The entirety of this basin is used for agricultural
practices with a small portion to the west covered with mountains
and forest.
Lake Basin Characteristics
Goose is a medium sized lake with a surface area of 245.20
acres. The perimeter was figured at 17,792 by the GIS system.
The deepest point was measured at 11 feet. The lake is
surrounded by Aspen.
The elevation is 5,172 feet. The water level is dependent
on the amount of precipation in the preceding year.
34

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Water Quality
The water quality of Goose Lake was monitored sparingly
through the years of 1966-77 with the results placed in the
Water Quality Management Plan of the Blackfeet Tribe. The
Blackfeet Environmental Office monitored Goose Lake again in 1993
and entered results in this report.
Goose Lake is well buffered, freshwater water body. The
water hardness is relatively low. The main ions were the
magnesium and calcium cations (Table 3).
Because of the moderate levels of nutrients and chlorophyll
a, Goose lake would be classified as mesotrophic, but additional
testing would be needed to prove it.
Biological Characteristics
Fish:
Goose lake is home to the brook trout.
35

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Table 1. Characteristics of Goose Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Cobbly, Gravelly, Stony, and
Light Clay Loams. (Loam).
Unavailable
Unavailable
Northern Rockies, Montana
Valley and Foothill Prairies
Aspen: Bearded Wheatgrass,
Rough Fescue, Bluebunch
Wheatgrass
Unknown
Unknown
36

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Table 2. Characteristics of Goose Lake.
elevation (ft.)
5,172.00
surface area (acres)
245.20
volume (acre-ft.)
Unknown
maximum depth (ft.)
11.0
mean depth (ft.)
Unknown
shoreline length (ft.)
17,793.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-24"
mean residence time (yr.)
Not available
control structure
None
37

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Table 3. Major ions and related water quality variables for Goose
Lake. Average concentrations in mg/L; pH in pH units. A sample
was collected from euphotic zone on 19 August 1993.
1992	1993
	Mean	Mean
pH (range)			9.34
alkalinity (mg/L CaCo3)			123.20
conductivity (umhos/cm)			210.00
turbidity (NTU)			2.92
dissolved oxygen			7.45
total suspended solids				
Ca			16.96
Mg			22.92
K			2.07
Na			3.4 0
C1				
S04				
38

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Goose
Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 19 August 1993.
1992	1993
Mean	Mean
45.52
5.92
< 2
11.19
31 9"
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
39

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Horse Lake
Horse Lake is found by traveling thirteen miles north of
Browning on the Duck Lake Road or as it is sometimes called BIA
Highway 464, turn west on a gravel road beside the Milk River, go
two miles up this road, and the lake is located between Toad
Creek and the Milk River. Horse Lake sits in a pocket up near
the continental divide with the west shore tribally owned and the
rest of shoreline in fee hands.
This lake is not used as a recreational lake. It is very
hard to access in dry or wet weather. Horse Lake is primarily
utilized for stock watering. It is believed that Horse Lake was
named for a horse that entered this lake years ago and did not
return. The lake was dry at the time.
Drainage Basin Characteristics
Horse Lake is only one of two lakes which reside within the
boundaries of the Milk River drainage basin. It is located in
the south western half of this basin. Horse Lake is charged by
run off, ground water, and one intermitted stream entering from
the north end of the lake.
Horse Lake coincides in the Montana Valley and Foothill
Prairies Ecoregion. The main vegetation around this lake is the
western wheatgrass and blue bunch wheatgrass. The soils consist
of light clay, clay,' and silty clay loams. Also, shale can be
found in the area.
The drainage basin has forest and mountains to the west with
ranching and farming becoming more prevalent to the east. There
are no communities in this basin.
Lake Basin Characteristics
Horse Lake is a shallow lake with the deepest point measured
in 1993 at 7 feet. The measurement was taken at the middle of
the lake. The surface area of Horse Lake is approximated at 238
acres. The shoreline is covered with prairie grass type
vegetation with the north shore having a sandy beach.
The elevation of Horse Lake was measured at 4,841 feet by
the USGS. The volume of water available for stock is controlled
by the amount of precipation in the preceding year.
40

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Water Quality
Horse Lake was monitored in 1993 by the Blackfeet
Environmental Office under Sec. 314 of the Clean Water Act.
Horse is a fresh water lake, that is well buffered. The
conductivity is highly elevated indicating a separation of salts
in this water body. Sodium (anion) concentrations are very high.
The highest cation content in Horse is the sulphates.
The largest concentration of nutrients in Horse Lake is the
phosphates. The nitrogen and chlorophyll a levels are quite low.
Thus, Horse Lake would be classified as mesotrophic because of
the chlorophyll a levels are lower in this lake than in lakes
with similar total phosphorus concentrations, but again further
testing is needed to prove assessment.
Biological Characteristics
No data available at this time.
41

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Table 1. Characteristics of Horse Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Light Clay, Clay, and Silty
Clay Loams. Also, Loam and
Shale.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Western Wheatgrass, Blue
Bunch Wheatgrass
Unknown
Unknown
42

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Table 2. Characteristics of Horse Lake.
elevation (ft.)
4,841.00
surface area (acres)
238.00
volume (acre-ft.)
Unknown
maximum depth (ft.)
7.0
mean depth (ft.)
unknown
shoreline length (ft.)
12,899.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
43

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Table 3. Major ions and related water quality variables for Horse
Lake. Average concentrations in mg/L; pH in pH units. A sample
was collected from euphotic zone 2 September 1993.
1992	1993
	Mean	Mean	
pH (range)			5.70
alkalinity (mg/L CaCo3)			1,122.00
conductivity (umhos/cm)			2,150.00
turbidity (NTU)			5.70
dissolved oxygen			8.25
total suspended solids			2.45
Ca			12.20
Mg			52.91
K			10.96
Na			509.66
CI			16.65
S04			138.64
44

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Horse
Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 2 September 1993.
1992	1993
Mean	Mean
60.97
< 5
2.39
2.34
4 ' 9"
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
45

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Cuii Bant
Drainage B asia

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Guardipee Lake
Guardipee Lake is situated nineteen miles east of Browning
on US Highway #2, turn south on dirt road for three miles to
Mission Lake, and then head west for three more miles. A guide
would be needed to access this lake since roads leading to it are
not well defined. Guardipee is surrounded by rolling hills.
The land encircling Guardipee Lake is in trust. The
Guardipee family owns land around this lake, and this is where
the name came from. There is definitely no recreational
activities or any other uses of its waters. Guardipee Lake was
once a major stock watering hole for Reservation cattle, but
careless farming practices turned this lake into a dead lake.
The lake is fenced off as to keep everything out.
Drainage Basin Characteristics
Guardipee Lake is located in the south central portion of
the Cut Bank drainage basin. It is charged by run off, ground
water, and a small stream which is fed by Lamott springs on the
west side of lake. There are no outlets.
Guardipee Lake sets in the Montana Valley and Foothill
Prairies Ecoregion. Green needlegrass and needle & thread are
the dominant vegetation in surrounding area with clay and cobbly
loam soils supporting them.
The far western section of this drainage basin is covered
with mountains and forest. The central area is more urbanized
where the communities of Browning and Blackfoot can be found with
ranching being the main land use. The eastern portion is
dominated by farming applications.
Lake Basin Characteristics
Five feet was the deepest point measured on Guardipee Lake.
Guardipee is a shallow lake with very poor water quality. It has
a surface area of 81.60 acres with a shoreline length of 10,387
feet. Grasses, banks, and rocky beaches make up the shoreline
around Guardipee Lake.
The elevation of Guardipee is 4,046 feet. The contributing
factors to water levels would be runoff and small stream on west
side.
46

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Water Quality
Guardipee Lake was monitored in 1993 by the Blackfeet
Environmental Office with ensuing data being placed in this Clean
Lakes Report.
Guardipee has extremely poor water quality due to farming
practices in the area. The conductivity is excessively high, and
thus pointing to enormous separation of salts (ions) in the water
of this lake. Because of salt content in lake, Guardipee is a
saline lake. All of the cation and anion concentrations are way
above normal and are most likely due to surface and ground water
runoff into the lake. All of these values are of concern to our
office. The sulphates, sodium, and magnesium levels are more
prevalent or in excess than other ions (Table 3). The high value
of Total Suspended Solids indicates that the water is very
turbid. The source of contamination is probably linked to use of
land in the area.
The Total Phosphorus (TP)content is very high and it is
certain that TP is coming directly off the clay particles
comprising the TSS. The Chlorophyll a concentration is also high
with secchi reading very low. The combination of above
contributors does help determine trophic status of lake, but
again further analysis would be needed to assess Guardipee Lake.
At this time, Guardipee would be a hyper-eutrophic lake.
Biological Characteristics
No data available at this time.
47

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Table 1. Characteristics of Guardipee Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay or Cobbly Loam
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Green Needlegrass, Needle
and Thread
Unknown
Unknown
48

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Table 2. Characteristics of Guardipee Lake.
elevation (ft.)
4,046.00
surface area (acres)
81.60
volume (acre-ft.)
Unknown
maximum depth (ft.)
5.0
mean depth (ft.)
Unknown
shoreline length (ft.)
10, 387 .00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
10-14"
mean residence time (yr.)
Not available
control structure
None
49

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Table 3. Major ions and related water quality variables for
Guardipee Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 2 September 1993.
1992
Mean
1993
Mean

pH (range) 	
9.26

alkalinity (mg/L CaCo3) 	
67.30

conductivity (umhos/cm) 	
15,000
.00
turbidity (NTU) 	
16.0

dissolved oxygen 	
8.0

total suspended solids 	
46.0

Ca 	
107.52

Mg 	
1,324.
74
K 	
213.18

Na 	
4,077.
31
CI 	
477.60

S04 	
14,679
.91
50

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Table 4. Nutrient, chlorophyll a and Secchi depth data for
Guardipee Lake. Average concentrations in ug/L. A sample was
collected from the euphotic zone on 2 September 1993.
1992	T993
Mean	Mean
306.88
12.63
<	2
30.53
<	1'
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
51

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Hidden Lake
Hidden Lake is located north of the community of Starr
School on what is referred to as Starr Flat. Hidden can be
accessed by traveling two and a half miles up this flat. Hidden
sits on the prairie grasslands.
Hidden Lake resides on private property. It is one of the
easier lakes to access. Hidden is primarily a fishing lake with
a few garbage cans on the south shore for sanitary purposes.
There is one residence in the immediate area which is located a
mile to the west of Hidden Lake.
Fishing and picnicking are the main activities associated
with Hidden Lake.
Drainage Basin Characteristics
Hidden Lake is positioned in the west central region of the
Cut Bank drainage basin. Hidden Lakes volume is dependent upon
run off, ground water, and a small irrigation ditch on the south
side. There is no outlet.
Montana Valley and Foothill Prairies Ecoregion is the
environment in which Hidden Lake can be found. Under normal
conditions, Rough fescue is the dominant vegetation with the soil
type being clay, gravelly clay, and gravelly clay loams.
Mountains and forest project into the sky on the west side
of drainage basin while ranching and farming intensify to the
east.
Lake Basin Characteristics
Hidden Lake is a semi-deep water body with the deepest spot
measured at 19 feet in 1993. The surface area, of Hidden Lake,
is estimated at 49.20 acres with a parameter of 5,472 feet.
Uncultivated shortgrass prairie is the type of land which
surrounds Hidden Lake.
Hidden Lake has an elevation of 4,616 feet. The amount of
water in lake is governed by precipation and flow from irrigation
ditch.
52

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Water Quality
A few parameters were monitored in 1980 by US Fish and
Wildlife Service and data was subsequently entered into Water
Quality Management Plan of the Blackfeet Tribe. More intense
monitoring of Hidden Lake was done in 1993 by the Blackfeet
Environmental Office and results are entered into this report.
Hidden Lake is a well buffered, freshwater lake. It is
reasonably alkalinize due to pH of 9.82 (Table 3). The content
of calcium and magnesium indicate a moderate hardness to the
water. The dominant ions are the cations of magnesium and
sodium.
The trophic status of Hidden Lake would fall under either
mesotrophic or eutrophic category. Because of the somewhat high
concentrations of nutrients and chlorophyll a, eutrophic status
would fit the definition of Hidden Lake, but further monitoring
should be done to prove this assessment.
Biological Characteristics
Fish:
Hidden Lake contains the rainbow trout, brook trout, and the
white sucker. This lake is planted annually, but due to the
owner not allowing right of way, this lake might not be stocked
in the coming years.
53

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Table 1. Characteristics of Hidden lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay, Gravelly Clay, and
Gravelly Sandy Clay Loams
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Rough Fescue
Unknown
Unknown
54

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Table 2. Characteristics of Hidden Lake.
elevation (ft.)
4,616.00
surface area (acres)
49.20
volume (acre-ft.)
Unknown
maximum depth (ft.)
19.0
mean depth (ft.)
Unknown
shoreline length (ft.)
5,472.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
54

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Table 3. Major ions and related water quality variables for
Hidden Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 25 August 1993.
1992	1993
	Mean	Mean
pH (range)			9.82
alkalinity (mg/L CaCo3)			550.00
conductivity (umhos/cm)			819.00
turbidity (NTU)			2.40
dissolved oxygen			10.25
total suspended solids			3.38
Ca			21.65
Mg			60.08
K			3.91
Na			98.79
CI			5.07
S04			5.05
55

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Hidden
Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 25 August 1993.
1992	1993
Mean	Mean
55.32
27.84
7.37
13.87
6'
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
56

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Hope Lake
Hope is a small lake which is set on the eastern edge of the
Blackfeet Reservation. It can be reached by taking US Highway #2
seven miles west of the town of Cut Bank, turn north on Henderson
Road for two miles, and then turn east on dirt road for another
mile. Hope sits in the middle of farm land.
There are a number of activities associated with this lake.
Stock watering is the principal use of Hope Lake, but fishing and
irrigation are also employed there.
The Blackfeet Fish and Game plant rainbow trout in Hope Lake
on a regular basis.
Drainage Basin Characteristics
Hope is the easterly most lake on the reservation, and is
set in the Cut Bank drainage basin. Hope is charged by ground
water and an irrigation ditch. There is very little runoff. On
the east end of lake, water is pumped out and used for
irrigation.
The Montana Valley and Foothill Ecoregion is the area which
Hope Lake is engraved in. Green needle grass and rough fescue
are the vegetation normally seen in this area with clay, gravelly
clay, and gravelly sandy clay loams soils supporting these flora.
The mountains can be seen in the west with agriculture
becoming more prominent to the east.
Lake Basin Characteristics
The deepest point surveyed in 1993 was 12 feet at the middle
of the lake. The surface area was measured at 68.80 acres with a
perimeter of 6,969 feet. Hope Lake is surrounded by tilled land
which is in fee status.
This is one of the lower lakes on the Blackfeet Reservation
at 3,877 feet. The water volume is controlled by irrigation turn
outs to and from the lake.
57

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Water Quality
Monitoring of Hope Lake was done by the Blackfeet
Environmental Office under Sec. 314 of the Clean Water Act with
results documented in this report.
Hope is a well buffered, freshwater lake. The turbidity and
total suspended solids were moderately elevated indicating lots
of sedimentation in water. Hope has a mediocre content of
calcium and magnesium which places the hardness of water in the
relative low category. Sulphate and calcium are the dominant
ions (Table 3).
Total phosphorus is very high. Also, the contents of
nitrogen and Chlorophyll a levels are slightly raised. These
heightened concentrations in junction with low secchi reading
would signify that Hope is a eutrophic lake.
Biological Characteristics
Fish:
The fish fauna residing in Hope Lake are the rainbow trout,
brook trout, and the white sucker.
58

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Table 1. Characteristics of Hope Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay, Gravelly Clay, and
Gravelly Sandy Clay Loams.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Green Needlegrass, Rough
Fescue
Unknown
Unknown
59

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Table 2. Characteristics of Hope Lake.
elevation (ft.)
3,877.00
surface area (acres)
68.80
volume (acre-ft.)
Unknown
maximum depth (ft.)
12.0
mean depth (ft.)
Unknown
shoreline length (ft.)
6,969.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
i—1
1
O
T	1
mean residence time (yr.)
Not available
control structure
None
60

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Table 3. Major ions and related water quality variables for Hope
Lake. Average concentrations in mg/L; pH in pH units. A sample
was collected from euphotic zone on 27 August 1993.
1992	T993
	Mean	Mean	
pH (range)			8.75
alkalinity (mg/L CaCo3)			154.00
conductivity (umhos/cm)			416.00
turbidity (NTU)			12.90
dissolved oxygen			8.21
total suspended solids			8.60
Ca			34.02
Mg			13.90
K			2.01
Na			25.73
CI			4.81
S04			55.49
61

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Hope
Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 27 August 1993.
1992	TW3
Mean	Mean
124.20
36.98
12.21
23.16
2*
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
62

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Kipp Lake
Kipp lake can be reached by turning off at Blackfoot on US
Highway #2, ten miles east of Browning and twenty five miles west
of Cut Bank. Kipp is located in rolling hill type terrain with
the Rocky Mountains visible twenty miles to the west.
The land surrounding Kipp Lake is currently being employed
in the form of ranching and farming. Half of the north east
shore is in fee status with the remainder of the lake shore in
the possession of the Blackfeet Tribe. An outhouse and a hand
water pump are the only luxuries available to you at this lake.
Kipp Lake got its name from a man who ran a trading post
near the lake in the early 1900's. His name was Joe Kipp. He
obtained the land around the lake when the 1924 Allotment Act was
inacted.
Kipp Lake is used primarily as a fishing lake year around.
Drainage Basin Characteristics
Kipp Lake is located in the Cut Bank drainage basin, which
is the largest basin on the reservation, but has the second
lowest output of measured run off of the four basins. Kipp is
charged by run off, ground water, and one intermitted stream on
the west end. Also, a turn out from Willow Creek is used to
charge Kipp Lake on the northwest side. A turn out on the north
end is used to release water back into Willow Creek for stock
watering purposes.
Kipp Lake is embedded in the Montana Valley and Foothill
Prairies Ecoregion. The terrain immediately surrounding the lake
is close to being level, but does have a slight rise ( 0-5%
slope). The riparian soils around the lake consist of various
loams and sands with the influential vegetation being green
needlegrass and needle/thread.
The drainage basin is covered with grass-type vegetation
extending out from Kipp Lake. Cattle use Kipp as a source of
drinking water. Agriculture dominates this drainage basin.
Lake Basin Characteristics
Kipp Lake is very shallow with 15 feet being the deep point
measured straight across from the dock. The surface area of Kipp
is 311.60 acres with a perimeter of 18,480 feet. The entirety,
of this lake, can be accessed for fishing and stock watering
purposes. Swimming was once a big recreational activity on Kipp
Lake, but excess weeds became to numerous.
Kipp Lake has an elevation of 4,106 feet. The level of
water in Kipp Lake depends on run off and ground water, but can
be raised or lowered when turn outs from Willow Creek are
opened/closed.
63

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Water Quality
Kipp Lake was monitored in 1967 for a few parameters and
this data was entered in the 1981 Water Quality Management Plan
of the Blackfeet Tribe. The Blackfeet Environmental Office
measured twenty one parameters in this lake in 1992 and 1993
under Sec. 314 of the Clean Water Act.
The high sulphate values should be looked into with the
source hopefully being found and then eliminated. The high
sulphate concentrations are causing a bad smell to the lake. The
higher magnesium levels are a good indicator that there is a
relative hardness to the water. The elevated values of
conductivity, turbidity, and total suspended solids points to
alot of particles and ions in water sample (table 3).
As indicated by the enormously heightened nitrate, nitrite,
and ammonia levels, algae growth is running rampant in this lake.
Also, chlorophyll a is extremely high, and is important for new
growth in algal cells. Examining the data available to us, Kipp
Lake's trophic status would be called hyper-eutrophic.
Biological Characteristics
Fish:
Kipp lake contains three species of fish. They include the
rainbow trout, white sucker, and longnose sucker. The rainbow
trout is planted annually.
64

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Table 1. Characteristics of Kipp Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay, Cobbly, Gravelly Clay,
and Silty Clay Loams.
(Loam). Cobbly and Gravelly
Sand.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Green Needlegrass, Needle
and Thread
Unknown
Unknown
65

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Table 2. Characteristics of Kipp Lake.
elevation (ft.)
4,106.00
surface area (acres)
311.60
volume (acre-ft.)
Unknown
maximum depth (ft.)
15.0
mean depth (ft.)
unknown
shoreline length (ft.)
18,480.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
10-14"
mean residence time (yr.)
Not available
control structure
None
66

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Table 3. Major ions and related water quality variables for Kipp
Lake. Average concentrations in mg/L; pH in.pH units. Samples
were collected from euphotic zone once on 27 October 1992, and
twice in 1993 on 2 August & 11 October. There were four grab
samples obtained at each visit.

1992
Mean
1993
Mean
pH (range)
9.23
9.03
alkalinity (mg/L CaCo3)
	
240.90
conductivity (umhos/cm)
	
762.00
turbidity (NTU)
7.66
9.52
dissolved oxygen
8.80
8.70
total suspended solids
6.97
5.93
Ca
29.19
29.05
Mg
63.93
52.80
K
8.75
8.99
Na
99.27
64.30
CI
14.48
11.58
S04
14.48
169.60
67

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Kipp
Lake. Average concentrations in ug/L. Samples were collected
from the euphotic zone once on 27 Oct. 1992, and twice in 1993 on
2 August & 11 October. There were four grab samples obtained at
each visit.

1992
1993

Mean
Mean
total phosphorus
87.49
45.19
NH3-N
41.87
119.44
N02/3
65.55
185.50
chlorophyll a
1.04
57.79
secchi depth (ft)
3'2"
8'8"
68

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Mission Lake
Mission Lake is the biggest lake in the Cut Bank drainage
basin. The four mile dirt road leading to Mission Lake can be
reached by driving seventeen miles east of Browning on US Highway
2. Also, the dirt road can be accessed by going eighteen miles
west of Cut Bank on US Highway 2. Mission is located in a green
valley in the south central part of the Reservation.
Mission lake has no structures about its shoreline, but it
does have a hand pump for water on the north central side. Also,
trash cans are strategically placed on the north side which are
maintained by Blackfeet Fish & Game. The entirety of land
surrounding Mission is in trust.
Mission lake is a haven for the big time fisherman. This
lake draws anglers from Canada and throughout the United States.
Mission was featured as one of the best lakes for fishing in the
country on a National Televised Show. Recreational activities are
limited to fishing on this lake because of the weed problem.
Mission Lake houses numerous waterfowl during their
migrating rituals.
Drainage Basin Characteristics
Mission Lake is charged by run off and ground water with no
tributaries contributing to its volume. Mission does have a turn
out on the east end of the lake which allows for cleansing of
this water body. Two Medicine irrigation canal runs parallel to
the lake on the north side and can possible charge Mission.
Montana Valley and Foothill Prairies Ecoregion is the home
of Mission Lake with the riparian soils consisting of clay and
cobbly loams. Under normal conditions, green needlegrass and
needle & thread vegetation are the dominant species.
The land basin extending out from Mission Lake is used for
farming to the north and east, and ranching to the south and
west. Although, some farming is occurring west of the lake.
Lake Basin Characteristics
Mission Lake has a measured surface area of 755 acres with
the deepest point being 33 feet straight outward from the water
pump on the west side. The shoreline is substantially long at
44,851 feet with range land dominating its surroundings. Cattle
owners utilize Mission for stock watering throughout the summer
while the fisherman uses it year around.
The USGS surveyed the elevation of Mission Lake at 3,954
feet. The water levels tend to variate with amount of
precipation that year.
69

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Water Quality
Mission Lake was periodically monitored from 1955-80 and the
resulting data entered in the 1981 Water Quality Management Plan
of the Blackfeet Nation. Mission was monitored twice in 1993
under Sec. 314 of the Clean Water Act.
The water in Mission Lake is well buffered and very hard.
The dominant ions being sodium and sulphate. The transparency is
often poor because of the dense algal growth.
The nutrients increased from August to November in 1993 with
Chlorophyll a decreasing at the same time. The high Total
Phosphorus values are a good indicator that there is algal
abundance in this lake. It is very difficult to place a trophic
label on this lake without further testing, but there is
definitely a substantial amount of nutrients in this lake.
Biological Characteristics
Fish:
Mission Lake houses the rainbow trout, burbot, walleye-
sauger hybrid, and white sucker. Rainbow trout is the primary
species and thus stocked annually.
70

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Table 1. Characteristics of Mission Lake drainage basin.
area (excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay and Cobbly Loam.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Green Needlegrass, Needle
and Thread
Unknown
Unknown
71

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Table 2. Characteristics of Mission Lake.
elevation (ft.)
3,954.00
surface area (acres)
755.00
volume (acre-ft.)
Unknown
maximum depth (ft.)
33.0
mean depth (ft.)
unknown
shoreline length (ft.)
44,851.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
10-14"
mean residence time (yr.)
Not available
control structure
None
72

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Table 3. Major ions and related water quality variables for
Mission Lake. Average concentrations in mg/L; pH in pH units.
Samples were collected from euphotic zone twice in 1993, once on
2 August and once on 11 October. Four grab samples were collected
at each visit.
m2

Mean
Mean
pH (range) 	
8.94
alkalinity (mg/L CaCo3) 	
169.40
conductivity (umhos/cm) 	
1,319.00
turbidity (NTU) 	
3.17
dissolved oxygen 	
8.08
total suspended solids 	
3.25
Ca 	
53.17
Mg 	
68.26
K 	
3.94
Na 	
151.69
CI 	
10.89
S04 	
518.29
73

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Table 4. Nutrient, chlorophyll a and Secchi depth data for
Mission Lake. Average concentrations in ug/L. Samples were
collected from the euphotic zone twice in 1993, once on 2 August
and once on 11 October. Four grab samples were collected at each
visit.
TW1	1993
Mean	Mean
58.81
28.04
14.54
1.83
4'3"
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
74

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No Chief Lake
No Chief is a very small lake which is located four miles
south west of Browning on BIA Highway #1. It is found in the
rolling plains of the Blackfeet Reservation. The shoreline is
covered with grasses and the east shore is the only access onto
the water. The lake and surrounding area are owned by the
Blackfeet Tribe.
There are no recreational activities associated with No
Chief Lake. The lake is used mainly as a place to water
livestock.
Drainage Basin Characteristics
No Chief rests on the southern boundary of the Cut Bank
drainage basin. Run off and ground water are the main sources of
charging for this lake. No Chief does not have an outlet for
water flow.
No Chief Lake is situated in the Montana Valley and Foothill
Prairies Ecoregion. Rough fescue is the dominant vegetation with
clay and loam soils surrounding the lakes perimeter.
Forest and mountains dominant the far west edges of this
drainage basin. Farming and ranching cover the rest of this
basin. Also, Browning is located in this watershed.
Lake Basin Characteristics
No Chief is the most shallowest lake that was measured in
1993 by Blackfeet Environmental Office. The surface area
covering No Chief is 72.60 acres with a shoreline of 7,315 feet.
Four feet was the deepest point in the lake. No Chief sits in
the high rolling hills of the Blackfeet Reservation.
The lake called No Chief abides at an elevation of 4,931
feet. The water level has dramatically been reduced over the
years as evident of high cut banks.
75

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Water Quality
The water quality of No Chief Lake was monitored once in
1973 and results were placed in Water Quality Management Plan of
the Blackfeet Tribe. The Blackfeet Environmental Office
continued monitoring in 1993 under Sec. 314 of the Clean Water
Act.
No Chief is a well buffered lake. The dissolved oxygen is
rather high indicating oxygenated groundwater. The dominant ions
are sulphate and magnesium. There is some hardness to the water
as evident by calcium and magnesium levels (Table 3).
The moderate concentrations of nutrients in No Chief Lake
along with a low content of chlorophyll a is a beneficial aid in
determining the status of this lake. At this time, No Chief
would be considered a mesotrophic lake because of preceding
values (Table 4).
Biological Characteristics
No data available at this time.
76

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Table 1. Characteristics of No Chief lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay, Cobbly, and Stony
Loams. Loam and Clay.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Rough Fescue
Unknown
Unknown
77

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Table 2. Characteristics of No Chief Lake.
elevation (ft.)
4,931.00
surface area (acres)
72.60
volume (acre-ft.)
Unknown
maximum depth (ft.)
4.0
mean depth (ft.)
Unknown
shoreline length (ft.)
9,315.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
78

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Table 3. Major ions and related water quality variables for No
Chief Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 25 August 1993.
1992
1993
Mean
Mean
pH (range) 	
8.58
alkalinity (mg/L CaCo3) 	
244.20
conductivity (umhos/cm) 	
854.00
turbidity (NTU) 	
1.30
dissolved oxygen 	
12.20
total suspended solids 	
2.14
Ca 	
46.78
Mg 	
63.07
K 	
17.17
Na 	
58.57
CI 	
8.01
S04 	
228.78
79

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Table 4. Nutrient, chlorophyll a and Secchi depth data for No
Chief Lake. Average concentrations in ug/L. A sample was
collected from the euphotic zone on 25 August 1993'.
1992	1993
Mean	Mean
45.22
17.30
< 2
1.10
3'3"
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
80

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Railroad Lake
Railroad is a very small lake which is located a few miles
south west of Browning on US Highway #2. When you reach this
point turn to the south, the lake is now in view beside the train
tracks. Railroad Lake sits in a coulee with prairie grasslands
surrounding it.
A dirt road runs into Railroad Lake from the north side with
railroad tracks passing by it on the east side. An old house
sits a quarter of a mile to the north of 'Railroad Lake. The land
surrounding this lake is in trust.
There are no recreational occurrences happening at Railroad
Lake. Livestock watering is the only activity associated with
this lake.
Drainage Basin Characteristics
Railroad Lake sits in the southern section of the Cut Bank
drainage basin. There are no tributaries flowing into Railroad
Lake. This lake is charged by run off and ground water with
excess water exiting on the east end, and eventually depositing
into Depot Coulee Creek.
Railroad Lake rests in the Montana Valley and Foothill
Prairies Ecoregion with rough fescue vegetation surrounding its
perimeter. The soils are comprised of loams and clay.
The western area of the drainage basin entails the mountains
and forest. The central area consists of ranching and two towns
(Browning and Blackfoot). The eastern area is predominantly used
for farming.
Lake Basin Characteristics
The deepest point sampled in 1993 was 7 feet. Railroad Lake
has an elevation of 4,500 feet. Precipation controls the volume
of water trickling into Railroad Lake. The shoreline is
surrounded by grassland and trodden cattle paths.
81

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Water Quality
Some vague monitoring of Railroad Lake was done in 1966 with
results published in the Blackfeet Tribes 208 Water Quality
Management Plan. More indepth monitoring was accomplished by the
Blackfeet Environmental Office in 1993 and is documented in this
report.
Railroad Lake is a moderately buffered lake with lots of
particles in water (total suspended solids). Because of the
elevated cations of magnesium and calcium (Table 3), the water is
considered hard. The anion sulfate is the most abundant of the
ions. This high concentration of sulfates is probably linked to
surface runoff.
The values of total phosphorus and ammonia indicate this
lake is somewhat rich in nutrients. The richness of nutrients
coupled with the elevated chlorophyll a content points in the
direction of an algae problem. It is very difficult to classify
the trophic status of Railroad Lake without further testing.
Biological Characteristics
No data available at this time.
82

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Table 1. Characteristics of Railroad Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay, Cobbly, and Stony
Loams. Loam and Clay.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Rough Fescue
Unknown
Unknown
83

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Table 2. Characteristics of Railroad Lake
elevation (ft.)
4,500.00
surface area (acres)
Not available
volume (acre-ft.)
Unknown
maximum depth (ft.)
7.0
mean depth (ft.)
Unknown
shoreline length (ft.)
Unavailable
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
84

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Table 3. Major ions and related water quality variables for
Railroad Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 25 August 1993.
1992	1993
	Mean	Mean	
pH (range)			8 . 60
alkalinity (mg/L CaCo3)			286.00
conductivity (umhos/cm)			924.00
turbidity (NTU)			7.50
dissolved oxygen			9.40
total suspended solids			15.33
Ca			76.51
Mg			51.83
K			3.08
Na			58.96
CI			3.53
S04			223.27
85

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Table 4. Nutrient, chlorophyll a and Secchl depth data for
Railroad Lake. Average concentrations in ug/L. A sample was
collected from the euphotic zone on 25 August 1993.
1992	1993
Mean	Mean
82.0
25.40
2.26
9.54
2'
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
86

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Sharp Lake
The best way to access Sharp Lake is by taking Highway 464
north of Browning for two miles, turn east on BIA Highway 13 for
six miles, next turn at the first gate past Cut Bank Creek bridge
to the right, and finally follow road for one mile to this water
body. Sharp Lake is set in the prairie grasslands of the
Blackfeet Reservation.
Sharp is a medium sized lake which is surrounded by a
barbwire fence. Thus, closing it off to the public. The lake
and riparian lands are tribally owned. Sharp Lake has a high
bank on the north and east sides with sandy shores on the
remainder of the lake. There is also three storage grain bens
situated on the north side of Sharp Lake.
There are no activities associated with Sharp Lake. The
water quality is very poor at this lake. The ecosystems that
once flourished around this lake are almost void.
Drainage Basin Characteristics
Sharp Lake rests in the central part of the Cut Bank
Drainage basin. It is charged by runoff and ground water. Also,
a small tributary flows into Sharp Lake from the west end charged
by the Cut Bank Creek. There is no outlet or outflow on this
lake.
Sharp Lake is nestled in the Montana Valley and Foothill
Prairies Ecoregion. The dominant vegetation is the rough fescue
with the soils being loams, silty clay, and soft shale.
The drainage basin involves mountains to the west with
ranching and farming increasing the farther east you travel. The
towns of Browning and Cut Bank are located in this basin along
with small community of Blackfoot.
Lake Basin Characteristics
Our office could not measure the depth of Sharp Lake because
we could not access the fence around it. The surface area, of
Sharp Lake, is 264.30 acres with a parameter of 14,423 feet.
The elevation of Sharp Lake is 4,195 feet according to the
topography map published by the Geological Survey in 1968. The
water has declined several feet over the last decade. The
biggest contributor to water volume would be runoff and ground
water.
87

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Water Quality
Sharp Lake was monitored by the Blackfeet Environmental
Office in 1993 under Section 314 of the Clean Water Act.
Sharp Lake is well buffered. Because of the extremely high
total suspended solids content, Sharp would be classified as a
saline lake. The conductivity reading would indicate a heavy
concentrations of salts. We did not get results back from
contract lab on metals because their instruments would not read
the murky water. We did get anion data which was abnormally
high.
In saline lakes, total phosphorus is not related to algal
growth because growth reguirements are met by supply. So, the
out greatly elevated values for total phosphorus in Sharp Lake
does not mean algae growth is running rampant. It is very
certain that the high total phosphorus concentrations are coming
directly off the clay particles comprising the total suspended
solids. There was no nitrogen values sent to us, but chlorophyll
a results very high. Hyper-eutrophic would be the term used to
define Sharp Lake due to the high nutrient and chlorophyll a
levels.
Biological Characteristics
No data available at this time.
88

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Table 1. Characteristics of Sharp Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay and Cobbly Clay Loams,
Silty Clay, and soft Shale
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Rough Fescue
Unknown
Unknown
89

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Table 2. Characteristics of Sharp Lake.
elevation (ft.)
4,195.00
surface area (acres)
264.30
volume (acre-ft.)
Unknown
maximum depth (ft.)
Unknown
mean depth (ft.)
Unknown
shoreline length (ft.)
14,423.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
90

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Table 3. Major ions and related water quality variables for Sharp
Lake. Average concentrations in mg/L; pH in pH units. A sample
was collected from euphotic zone on 27 August 1993.
1992	T993
	Mean	Mean	
pH (range)			9.22
alkalinity (mg/L CaCo3)			1,045.00
conductivity (umhos/cm)			1,990.00
turbidity (NTU)				
dissolved oxygen			8.40
total suspended solids			1,029.92
Ca				
Mg				
Na				
CI			77.74
S04			338.84
91

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Sharp
Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 27 August 1993.
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
1992	1993
Mean	Mean
6, 420.92
		58.71
92

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Whiskey John Lake
Whiskey John is located directly on the south side of US
Highway #2 five miles west of Browning. It is set on the foot
hills of the Rocky Mountains.
The land surrounding the shores of Whiskey John is in trust
or Blackfeet owned. This lake is not used for any recreational
purposes. Stock watering is its only application.
Drainage Basin Characteristics
Whiskey John rests on the south west boundary of the Cut
Bank drainage basin. It is charged by run off and ground water.
The east shore can be an outlet due to it being lower than the
rest of the water body.
Whiskey John Lake is situated in the Montana Valley and
Foothill Prairies Ecoregion. Rough Fescue is the main vegetation
found in this area with loam and clay soils supporting it.
The drainage basin has mountains to the west, and prairie
grasslands to the east with the communities of Browning and
Blackfoot residing in it.
Lake Basin Characteristics
Six feet was the deepest area measured on Whiskey John Lake
by the Blackfeet Environmental Office in 1993. The surface area
of this lake is only 23.74 acres. Grasses encompass the
shoreline with the east side open for stock watering.
The elevation of Whiskey John was surveyed at 4,957 feet.
Precipation is the main element in the volume of water at this
lake.
Water Quality
Water quality was tested in 1980 with ensuing results placed
in the Blackfeet Tribe's 208 Water Quality Management Plan. More
extensive monitoring of Whiskey John Lake was done by the
Blackfeet Environmental Office in 1993.
Whiskey John is a well buffered lake. The dissolved oxygen
is sort of high due to the shallowness of lake with oxygenated
groundwater more than likely to occur there. Sodium and
magnesium are the most numerous ions (Table 3). The water has a
low hardness to it based on content of cations.
The results (Table 4) obtained in 1993 are quite hard to
decipher. At this point, Whiskey John would be considered an
oligo-mesotrophic lake because of moderately high phosphate
content and low chlorophyll a concentration.
Biological Characteristics
No data available at this time.
93

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Table 1. Characteristics of Whiskey John Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay, Cobbly, and Stony
Loams. Loam and Clay.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Rough Fescue
Unknown
Unknown
94

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Table 2. Characteristics of Whiskey John Lake.
elevation (ft.)
4,957.00
surface area (acres)
23.74
volume (acre-ft.)
Unknown
maximum depth (ft.)
6.0
mean depth (ft.)
Unknown
shoreline length (ft.)
Unavailable
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
95

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Table 3. Major ions and related water quality variables for
Whiskey John Lake. Average concentrations in mg/L; pH in pH
units. A sample was collected from euphotic zone on 25 August
1993.
TW2	TMT
Mean	Mean
pH (range) 	-
9.
54
alkalinity (mg/L CaCo3) 	
352.00
conductivity (umhos/cm)
576.00
turbidity (NTU) 	
2.
60
dissolved oxygen 	
10
.70
total suspended solids 	
4.
13
Ca 	
14
.48
Mg 	
26
.62
K 	
7.
11
Na 	
89
.94
CI 	
3.
54
S04 	
0.
02
96

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Table 4. Nutrient, chlorophyll a and Secchi depth data for
Whiskey John Lake. Average concentrations in ug/L. A sample was
collected from the euphotic zone on 25 August 1993.
1992	TTO
Mean	Mean
40.47
7.75
< 2
1.69
5'
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
97

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Two M^eJicime
Drainage Basin

-------
South Alkali Lake
South Alkali Lake is very hard to access in dry or wet
weather. Alkali can be reached by going 17 miles south of Cut
Bank on Highway 358, and then turning west on a dirt road for
four miles. This is one of the largest lakes on the reservation
at a mile wide by a mile and a half long, but it is very shallow.
South Alkali is situated in a grassy valley.
This lake is tribally owned with some stock watering
occurring on its shores. South Alkali is known as a waterfowl
sanctuary. South Alkali received its name because of the
abundance of alkali in the soil about its shorelines.
Drainage Basin Characteristics
South Alkali Lake is situated at the foremost eastern
section of the Two Medicine drainage basin. Birch Creek canal
supplies South Alkali with a sufficient amount of water. The
water enters South Alkali on the south side of the lake.
The Montana Valley and Foothill Prairies Ecoregion is where
South Alkali Lake is located at. Under ordinary conditions, the
Western wheatgrass and Green needlegrass are the governing
vegetation. Clay and clay loams are the soils which can be found
in this drainage basin.
Mountains and forest can be located to the far west with
rangeland increasing in the middle of drainage basin. The area
immediately surrounding lake is mostly farm land.
Lake Basin Characteristics
South Alkali Lake is the largest lake in the Two Medicine
drainage basin. The surface area is measured at 1,014.50 acres
and shoreline length at 34,742 feet. We were 150 yards from the
south shore and measured the depth of South Alkali at 3 feet on
the 1 of September 1993. The shore line consist of sandy beaches
mixed with grassy type banks.
The elevation of South Alkali Lake is set at a relatively
low 3,786 feet. The quantity of water, in this lake, is
controlled by precipation and amount of water released into it by
Birch Creek canal.
98

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Water Quality
South Alkali was monitored in 1979 by US Fish and Wildlife
Service and again in 1993 by the Blackfeet Environmental office.
The extremely high conductivity reading in South Alkali
signifies a large amount of charged ions (anions & cations) in
the water. It is a highly buffered lake which has hard water.
The total suspended solids points to a very turbid lake. The
sulphate anion concentration, which is highly elevated, is
possibly linked to sulphates enter lake through surface run off
and ground water.
Because South Alkali has a high total phosphorus content, a
low nitrogen and chlorophyll a content, and a low secchi reading,
this indicates an algae abundance. At this time, South Alkali
would be called a mesotrophic lake because of the reasons stated
above, but there should be some extensive monitoring of this lake
to prove this assessment. The water is very green and scummy.
This could be from the wealth of algae or high particulate level
in this lake.
Biological Characteristics
No data available at this time.
99

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Table 1. Characteristics of South Alkali Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay and Clay Loam
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Western Wheatgrass, Green
Needlegrass
Unknown
Unknown
100

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Table 2. Characteristics of South Alkali Lake.
elevation (ft.)
3,786.00
surface area (acres)
1,014.50
volume (acre-ft.)
Unknown
maximum depth (ft.)
Not available
mean depth (ft.)
Unknown
shoreline length (ft.)
34,742.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
10-14"
mean residence time (yr.)
Not available
control structure
None
101

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Table 3. Major ions and related water quality variables for South
Alkali Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 1 September 1993.
1992	1993
Mean	Mean
pH (range) 	
9.
43
alkalinity (mg/L CaCo3) 	
431.20
conductivity (umhos/cm) 	
4,
500.00
turbidity (NTU) 	
73
.0
dissolved oxygen 	
8.
80
total suspended solids 	
37
.50
Ca 	
23
.16
Mg 	
74
.32
K 	
4.
26
Na 	
1,
279.16
CI 	
76
.21
S04 	
2,
133.08
102

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Table 4. Nutrient, chlorophyll a and Secchi depth data for South
Alkali Lake. Average concentrations in ug/L. A sample was
collected from the euphotic zone on 1 September 1993.
1992	1993
	Mean	Mean
total phosphorus			109.43
NH3-N			< 5
N02/3			< 2
chlorophyll a			3.57
secchi depth (ft)			< 1'
103

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Cooper Lake
Cooper is a tiny lake which rests in the high foothills of
the Rocky Mountains. It is located a half mile east of Lewis and
Clark National Park and almost on top of western boundary of the
Blackfeet Reservation. Cooper can be accessed by taking BIA
Highway #1 eight miles to the north of Heart Butte community, and
then turn west for 2.5 miles. A four wheel vehicle is definitely
needed to get to Cooper Lake.
Cooper is owned and stocked by the Blackfeet Tribe. The
land to the west is owned by the federal government with
remaining land in trust.
Cooper Lake received its name from the Cooper family who
lived near the lake in the 1930' s. It's original name was Many
White Horses Lake.
This lake is known for its cutthroat trout which the
Blackfeet Fish and Game plants there on a regular basis. Also,
in the summer, cattle use Cooper Lake as a water source.
Drainage Basin Characteristics
Cooper Lake rests on the west central fringe of the Two
Medicine drainage basin. It is charged by run off, ground water,
and a tributary on the north western side. There is no outlet on
this lake.
The Northern Rockies Ecoregion is where Cooper Lake is
situated. Under normal conditions, rough fescue is the grass in
this area. The soils consist of loams, silty clay, and rock
outcrops.
Cooper sits in the far western section of this drainage
basin with ranching progressing to farming the farther east you
travel. Heart Butte is the only community in this basin, and is
located in the southern half of basin.
Lake Basin Characteristics
Because we could not get boat up to lake, we did not measure
depth of Cooper Lake. This lake is very small with a surface
area of 31.40 acres and a shoreline length of 7,330 feet. Cooper
Lake is surrounded by a combination of Aspen, willow, and various
pines. Cooper rests at an elevation of 5,375 feet with its water
level affected by precipation.
104

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Water Quality
Cooper Lake was monitored by the Blackfeet Environmental
Office in 1993 with consequential results entered into this
report (Tables 3-4).
Cooper is a semi-buffered, freshwater lake with excellent
water quality. The hardness of the water is relatively low as
magnesium and calcium concentrations would attest to. These two
cations are also the main ions in Cooper (Table 3).
Because of the almost non-existent algae growth, low
nutrient content, and very low Chlorophyll a levels (Table 4),
Cooper Lake would be assessed as an oligotrophic lake.
Biological Characteristics
Fish:
Cooper lake contains Snake River cutthroat trout.
105

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Table 1. Characteristics of Cooper Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Stony and Cobbly Clay Loams.
Loam, Silty Clay, and Rock
Outcrops.
Unavailable
Unavailable
Northern Rockies
Rough Fescue
Unknown
Unknown
106

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Table 2. Characteristics of Cooper Lake.
elevation (ft.)
5,375.00
surface area (acres)
31.40
volume (acre-ft.)
Unknown
maximum depth (ft.)
Unknown
mean depth (ft.)
Unknown
shoreline length (ft.)
7,330.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
20" +
mean residence time (yr.)
Not available
control structure
None
107

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Table 3. Major ions and related water quality variables for
Cooper Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 30 August 1993.
1992	1993
	Mean	Mean
pH (range)			9.35
alkalinity (mg/L CaCo3)			93.50
conductivity (umhos/cm)			141.00
turbidity (NTU)			0.77
dissolved oxygen			8.60
total suspended solids			0.56
Ca			14.89
Mg			18.78
K			0.17
Na			1.64
CI			0.36
S04			2.38
108

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Cooper
Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 30 August 1993.
1992	1993
	Mean	Mean
total phosphorus			17.0
NH3-N			7.06
N02/3			< 2
chlorophyll a			0.56
secchi depth (ft)				
109

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Dog Gun Lake
Dog Gun Lake is located about one and a half miles up the
Hughes Trail. The Hughes Trail is situated four miles to the
west of the Heart Butte Cut Across. The Heart Butte Cut Across
is located thirteen miles south of Browning on BIA Highway #1.
Dog Gun is set inside the splendor of the Rocky Mountains.
The land surrounding Dog Gun Lake is under two different
ownerships. A portion of the southwest and northeast side is fee
lands with the balance of shoreline owned by the Blackfeet Tribe.
There are a couple of houses sitting a few hundred yards from
shore on the south end.
Dog Gun is known for its fishing by local residents. Dog
Gun is fished throughout the year.
Drainage Basin Characteristics
Dog Gun Lake lies on the far west fringes of the Two
Medicine drainage basin. The lake is charged by ground water and
alot of run off. Also, two perennial tributaries flow into Dog
Gun Lake. One unnamed stream enters from the west end and Deep
Creek emerges from the south. The outflow leaves Dog Gun on the
east end.
Northern Rockies Ecoregion is where Dog Gun Lake resides.
The most abundant vegetation around the lake is the rough fescue
with the soils being loams, silty clay, and rock outcrops.
This drainage basin consists of mountains to the west with
agriculture developing more in the easterly direction.
Lake Basin Characteristics
Dog Gun is a shallow lake which was measured at 9 feet by
the Blackfeet Environmental Office in 1993. The shoreline, of
Dog Gun Lake, was measured at 15,612 feet, and the surface area
at 124.40 acres. Most of the lake shore is covered with grasses.
The west and southwest shores do have some timber stands which
are the of the Aspen species.
Dog Gun has an elevation of 5,183 feet as was surveyed by
the USGS. The volume of water residing in this lake is regulated
by precipation.
no

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Water Quality
The monitoring of Dog Gun Lake has occurred twice in the
past twenty years. Once very moderately in 1974 by the US Fish
and Wildlife Service with data entered into Water Quality
Management Plan of Blackfeet Tribe, and once in 1993 by the
Blackfeet Environmental Office with data present in this report.
Dog Gun is a well buffered, freshwater lake. The
concentration of anions and cations are especially low. The
small contents of calcium and magnesium in water sample does
indicate that water is soft (Table 3).
There is elevated concentrations of phosphorus, ammonia, and
chlorophyll a. By examining the these value (Table 4), we can
determine that there is definitely algae growth in this lake. In
leu of these results, eutrophic status would best fit this lake.
There would have to be additional testing done to justify
assessment.
Biological Characteristics
Fish:
Dog Gun Lake contains a variety of fish species. The fish
fauna include the rainbow trout (which is planted annually),
brook trout, Arctic grayling, white sucker, and the fathead
minnow.
Ill

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Table 1. Characteristics of Dog Gun Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Stony and Cobbly Clay Loams.
Loam, Silty Clay, and Rock
Outcrops.
Unavailable
Unavailable
Northern Rockies
Rough Fescue
Unknown
Unknown
112

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Table 2. Characteristics of Dog Gun Lake.
elevation (ft.)
5,183.00
surface area (acres)
124.40
volume (acre-ft.)
Unknown
maximum depth (ft.)
9.0
mean depth (ft.)
Unknown
shoreline length (ft.)
15,612.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
20" +
mean residence time (yr.)
Not available
control structure
None
113

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Table 3. Major ions and related water quality variables for Dog
Gun Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 11 August 1993.
1992
1993
Mean
Mean
pH (range) 	
9.20
alkalinity (mg/L CaCo3) 	
81.40
conductivity (umhos/cm) 	
105.00
turbidity (NTU) 	
8.92
dissolved oxygen 	
6.90
total suspended solids 	
5.46
Ca 	
13.14
Mg 	
5.35
K 	
0.27
Na 	
3.61
CI 	
0.22
S04 	
1.50
114

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Dog
Gun Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 11 August 1993.
1992	T593
Mean	Mean
119.90
39.26
< 2
23.99
2'8"
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
115

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Four Horns Lake
Four Horns Lake is accessed by driving fifteen miles to the
south of Browning on US Highway 89 turning west on BIA Highway 4
for three miles, and then turn south on dirt road for three more
miles. Four Horns is the second biggest lake in the Two Medicine
drainage basin and is set in the prairies of the Blackfeet
Reservation.
Four Horns Lake was created in the 1920's to store water for
irrigation on the Badger-Fisher Flats. Tribal land circumscribes
the entirety of Four Horns Lake. A few trash cans, a pit toilet,
and a handpump are the only luxuries surrounding this lake. This
lake obtained its name from the family called Four Horns who were
allotted land around it.
Four Horns is known for its fishery. Stock watering,
fishing, and irrigation are the principle uses of Four Horn Lake.
Also, many species of water fowl utilize this lake as a resting
place during their seasonal migration.
Drainage Basin Characteristics
Four Horn Lake is positioned in the lower south eastern half
of the Two Medicine drainage basin. Two Medicine drainage basin
had the highest measured runoff in 1991 at an estimated 679,100
acre feet. Four Horn is charged by run off, a small intermitted
stream out of Jackson coulee to the south, and by a canal
carrying water from Big Badger creek on the west side. On the
east side of the lake, a turnout can be found which yields water
for irrigation purposes.
Four Horn Lake is located in the Montana Valley and Foothill
Prairies Ecoregion. The most prominent vegetation around this
lake is needle & thread and green needlegrass. Clay and cobbly
loams are the dominant riparian soils around this lake.
The land base surrounding Four Horn Lake has mountains and
range land to the west with agriculture dominating in the east.
Lake Basin Characteristics
The surface area, of Four Horn Lake, is 718.60 acres. There
was a bottom profile done by the US Fish and Wildlife Service in
1981 with the deepest point measured at 33 feet. The length of
the shoreline is 34,584 feet.
Four Horn has an elevation of 4,111 feet. The amount of
water available for irrigation practices is depended upon several
factors with the influx of water from Big Badger being the most
important one. Also, the volume of water in Four Horns is
controlled by the turnout on east side.
116

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Water Quality
The monitoring of Four Horn Lake was done in 1980 under the
Water Quality Management Plan of the Blackfeet Nation. Also, a
more intense measuring of parameters was completed in 1993 by the
Blackfeet Environmental Office under the Clean Water Act.
Four Horns is a well buffered, freshwater lake with the
dominant ions being sulphate, calcium, and magnesium. The water
is hard because of the elevated content of calcium and magnesium.
The extremely low nutrient and Chlorophyll a readings (Table
4) are good evidence that Four Horn Lake would be grouped in the
oligotrophic category, but subsequent testing would be necessary
to substantiate it.
Biological Characteristics
Fish:
Four Horn has a great fishery with the walleye being unique
to it. The lake also contains other species including the
rainbow trout, brown trout, mountain whitefish, and the white
suckers.
117

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Table 1. Characteristics of Four Horns Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay and Cobbly Loam.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Green Needlegrass, Needle
and Thread
Unknown
Unknown
118

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Table 2. Characteristics of Four Horns Lake.
elevation (ft.)
4,111.00
surface area (acres)
718.60
volume (acre-ft.)
Unknown
maximum depth (ft.)
23.0
mean depth (ft.)
Unknown
shoreline length (ft.)
34,584.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
10-14"
mean residence time (yr.)
Not available
control structure
None
119

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Table 3. Major ions and related water quality variables for Four
Horns Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 12 Augussst 1993.
1992
1993
Mean
Mean
pH (range) 	
8.47
alkalinity (mg/L CaCo3) 	
123.20
conductivity (umhos/cm) 	
400.00
turbidity (NTU) 	
1.81
dissolved oxygen 	
7.20
total suspended solids 	
2.02
Ca 	
46.39
Mg 	
27.59
K 	
0.81
Na 	
4.91
CI 	
0.40
S04 	
108.54
120

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Four
Horns Lake. Average concentrations in ug/L. A sample was
collected from the euphotic zone on 12 August 1993.
1992	TW3
Mean	Mean
7.10
6.34
< 2
0.32
12' 6"
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
121

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Magee Lake
Magee lake is situated six miles south of Browning on BIA
Highway #1. Travel down a dirt road east of this highway for one
mile, and this will take you directly to Magee lake. This lake
sits inside of rolling hills.
The only activity associated with Magee Lake is watering of
stock. It was stocked with rainbow in 1993, but is not heavily
fished. Magee Lake acquired its name from the Magee family who
own land around this small water body. There is a small area on
the south west shore that is fee land.
Drainage Basin Characteristics
Magee Lake is located in the north central portion of the
Two Medicine drainage basin. Magee is charged by run off, ground
water, and a small intermitted tributary on the west end. There
are no outlets on this lake.
Magee Lake is localized in the Montana Valley and Foothill
Prairies with rough fescue vegetation being dominant. The
riparian soils include clay, cobbly, and stony loams plus clay.
Magee is set in prairie grassland portion of the Blackfeet
Reservation.
Lake Basin Characteristics
Magee is a very small shallow lake with a surface area of
49.30 acres, and a shoreline length of 5,969 feet. The deepest
point found in 1993 was 8 feet by the Blackfeet Environmental
Office. Magee Lake is a major waterhole for livestock. The
affects of these animals on this lake are seen on trodden
shoreline and the water quality.
Magee Lake has an elevation of 4,676 feet. The main
contributor, to volume of water in Magee, would be the
precipation factor for that year.
122

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Water Quality
Magee was monitored in 1973 and data was entered into the
Water Quality Management Plan of the Blackfeet Tribe, and has
been measured only once since then by the Blackfeet Environmental
Office in 1993.
Magee has a water quality problem. The lake water is well
buffered with an enormous suspended particle problem determined
by extremely high conductivity readings, and heightened content
of cation values (Table 3). Sodium and Magnesium are the
dominant ions in Magee Lake.
The elevated concentrations of total phosphorus and ammonia
does represent an algal problem. Also, chlorophyll a is
moderately high thus indicating a wealth of algae. The high
content of nutrients in Magee Lake might come from runoff or
livestock wastes. Because this is a well nourished lake, Magee
would be considered an eutrophic water body although further
analysis would be needed to confirm it.
Biological Characteristics
Fish:
Magee Lake was stocked in 1993 with the rainbow trout
species. No other fish fauna is known to live there.
123

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Table 1. Characteristics of Magee Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Clay, Cobbly, and Stony
Loams. Loam and Clay.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Rough Fescue
Unknown
Unknown
124

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Table 2. Characteristics of Magee Lake.
elevation (ft.)
4,676.00
surface area (acres)
49.30
volume (acre-ft.)
Unknown
maximum depth (ft.)
OO
o
mean depth (ft.)
Unknown
shoreline length (ft.)
5,969.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
125

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Table 3. Major ions and related water quality variables for Magee
Lake. Average concentrations in mg/L; pH in pH units. A sample
was collected from euphotic zone on 18 August 1993.
T992	TM3
	Mean	Mean
pH (range)			8.93
alkalinity (mg/L CaCo3)			481.80
conductivity (umhos/cm)			2,250.00
turbidity (NTU)			5.46
dissolved oxygen			6.20
total suspended solids				
Ca			55.83
Mg			273.30
K			37.90
Na			269.82
CI				
S04				
126

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Magee
Lake. Average concentrations in ug/L. A sample was collected
from the euphotic zone on 18 August 1993.
IWI	F993
	Mean	Mean
total phosphorus			111.54
NH3-N			170.12
N02/3			6.33
chlorophyll a			10.26
secchi depth (ft)			5'10"
127

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Water Quality
There was very limited monitoring of Mittens Lake in 1977
with the few of results put in the Water Quality Management Plan
of the Blackfeet Tribe. Horse was monitored more extensively in
1993 by the Blackfeet Environmental Office.
Mittens Lake is well buffered, freshwater lake. The water
is moderately hard as values of calcium and magnesium can attest
to (Table 3). The main ions in this lake are magnesium and the
sulphates.
The concentrations of phosphorus, nitrogen, and chlorophyll
a are extremely low. These values along with the high secchi
reading would point in the direction of an oligotrophic lake, but
there are lots of weeds in this lake which might place Mittens in
another tropic status. More extensive monitoring would be needed
to classify this lake.
Biological Characteristics
Fish:
Mittens is known for its trophy trout. Rainbow trout is
stocked annually in this lake.
129

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Table 1. Characteristics of Mitten Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Cobbly, Gravelly, and Stony
Clay Loams.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Bluebunch Wheatgrass
Unknown
Unknown
130

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Table 2. Characteristics of Mitten Lake.
elevation (ft.)
4,743.00
surface area (acres)
186.40
volume (acre-ft.)
Unknown
maximum depth (ft.)
11.0
mean depth (ft.)
Unknown
shoreline length (ft.)
15,450.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
131

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Table 3. Major ions and related water quality variables for
Mittens Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 9 August 1993.
1992	T993
	Mean	Mean	
pH (range)			9.18
alkalinity (mg/L CaCo3)			176.00
conductivity (umhos/cm)			433.00
turbidity (NTU)			0.80
dissolved oxygen			8.00
total suspended solids			0.82
Ca			18.94
Mg			33.89
K			2.13
Na			23.96
CI			0.46
S04			70.07
132

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Table 4. Nutrient, chlorophyll a and Secchi depth data for
Mittens Lake. Average concentrations in ug/L. A sample was
collected from the euphotic zone on 9 August 1993.
1992	T993
Mean	Mean
16.0
9.97
< 2
0.40
10' 3 "
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
133

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Swift Reservoir
Swift Reservoir can be reached by taking US Highway 89 south
east out of Browning for approximately forty miles, and then turn
west on gravel road for another seventeen miles. This gravel
road is located a few miles north of Dupuyer, MT. Swift is a
medium sized lake which sits on the far southwest boundary of the
Blackfeet Reservation.
Most of Swift Reservoir lies within the Lewis and Clark
National Forest with the northern tip on Reservation lands.
Swift is used mainly for irrigation storage and flood control.
There is also some secondary benefits that include fishing,
boating, and waterfowl habitat.
Swift Reservoir is also known as Birch Creek Reservoir(Dam)
and was once an earth filled dam, but it was washed out in the
1964 flood. A new concrete dam was built in 1966.
Drainage Basin Characteristics
Swift Reservoir rests on the most southern part of the Two
Medicine drainage basin. It is charged by the North Fork and
South Fork of Birch Creek. The discharge of water exists out of
Swift Dam on the eastern side of reservoir.
Swift Reservoir is nestled in the Northern Rockies Ecoregion
with rough fescue vegetation being most prominent. Loams, silty
clay, and Rock Outcrops are the soils to be found in the
immediate area.
This drainage basin consists of the community of Heart Butte
in the southern portion, the Rocky Mountains protruding in the
west, and agriculture magnifying towards the east.
Lake Basin Characteristics
The reservoir is very deep at 90 feet. The surface area was
measured at 443.57 acres and shoreline length at 51,984 feet.
Mountain terrain surrounds most of this reservoir with the
concrete structure (dam) on the east side facing the prairies.
The elevation of Swift Reservoir is 4,884 feet. The volume
of water is controlled by Swift Dam. Water is regulated for
irrigation applications.
134

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Water Quality
Monitoring of water quality was initiated by the Blackfeet
Environmental Office in 1993 under Sec. 314 of the Clean Water
Act.
Swift Reservoir is a well buffered, freshwater water body.
The water is relatively hard due to the calcium and magnesium
content(Table 3). The water quality is excellent.
Nitrate and nitrite are the dominant nutrients in Swift
Reservoir, but the their concentrations are moderately low. This
inorganic form of nitrogen can influence the composition of the
algal community. The low content of nutrients along with small
Chlorophyll a levels and high secchi depth reading corresponds to
an oligotrophic lake.
Biological Characteristics
No data available at this time.
135

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Table 1. Characteristics of Swift Reservoir drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Stony and Cobbly Clay Loams
Loam, Silty Clay, and Rock
Outcrops.
Unavailable
Unavailable
Northern Rockies
Rough Fescue
Unknown
Unknown
136

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Table 2. Characteristics of Swift Reservoir.
elevation (ft.)
surface area (acres)
storage capacity (acre-ft.)
storage in 1992 (acre-ft.)
maximum depth (ft.)
mean depth (ft.)
shoreline length (ft.)
contol structure
dam height (ft.)
dam crest length (ft.)
dam crest elevation (ft.)
overflow spillway crest
elevation (ft.)
mean annual lake evaporation (in.)
mean annual precipation (in.)
mean residence time (yr.)
4,884.00
443.57
35,570.00
187,565
90.0
Unknown
51,984.00
concrete dam
205.00
560.00
4,883.50
4,886.00
Unknown
20" +
Not available
137

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Table 3. Major ions and related water quality variables for Swift
Reservoir. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 10 August 1993.
1992
1993
Mean
Mean
pH (range) 	
8.18
alkalinity (mg/L CaCo3) 	
143.00
conductivity (umhos/cm) 	
300.00
turbidity (NTU) 	
0.78
dissolved oxygen 	
8.40
total suspended solids 	
< 0.5
Ca 	
40.98
Mg 	
12.92
K 	
0.46
Na 	
0.81
CI 	
0.26
S04 	
16.08
138

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Table 4. Nutrient, chlorophyll a and Secchi depth data for Swift
Reservoir. Average concentrations in ug/L. Samples were
collected from the euphotic zone from 10 August 1993.
1992	T9§3
Mean	Mean
2.80
8.10
23.50
0.24
2 51 2 "
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
139

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North Twins Lake
North Twins Lake is located twenty miles south of Browning
on BIA Highway 1. Also, it can be reached by going five miles
north west of Heart Butte on the same highway. North Twins sets
in the foothills just below the magnificent Rockies.
North Twins Lake has a few wooden tables, cooking areas, and
trash cans to accommodate the recreationalist. The Blackfeet
Fish & Game monitors and cleans around the lake daily. The land
surrounding the lake is Tribally owned.
Many recreational activities are associated with North
Twins Lake. Fishing, swimming, picnicking, non-motorized
boating, and camping are some of activities which this lake has
to offer.
Drainage Basin Characteristics
North Twins Lake sits in the south central portion of the
Two Medicine drainage basin. This lake is charged by ground
water and run off. Also, water is yielded to this lake through a
culvert connecting it to South Twins Lake. An outlet can be
found on the west shore. The water which leaves this turnout
ends up in Badger Creek and consequently into the Two Medicine
River.
North Twins Lake is situated in the Montana Valley and
Foothill Prairies Ecoregion. The bluebunch wheatgrass is the
dominant species of vegetation found around this lake. The
riparian soils are comprised of cobbly, gravelly, and stony
loams.
The drainage basin consists of mountains and forest to the
south and west with range converting to farm land the further
east you travel into the basin.
Lake Basin Characteristics
This is a very shallow lake with the deepest point being
measured at 8 feet. Twins North Lake has a relatively small
surface area of 14.27 acres. The shoreline length was measured
at 4,217 feet. There are a few willows scattered on the south
west shore with the entirety of the lake encompassed with
grasses.
North Twins Lake has an elevation of 5,171 feet. The amount
of water entering from South Twins is a big factor in the volume
of water stored in this lake. Also, water exiting lake through
turnout on west side affects volume.
140

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Water Quality
North Twins Lake was initially monitored in 1966 and 1967
with the results being published in the 208 Water Quality
Management Plan of the Blackfeet Tribe. Monitoring was
reestablished in 1993 by the Blackfeet Environmental Office
through the Clean Lakes Program.
The moderately low concentrations of calcium and magnesium
signify that the water is slightly hard. The alkalinity value
indicates the lake is well buffered.
Analyzing the limited data, North Twins Lake would fall
under the classification of oligotrophic because of low
concentrations of nutrients, low chlorophyll a value, high secchi
reading, lack of algae, and the clearness of the water.
Biological Characteristics
Fish:
North Twins Lake is known for its rainbow trout which is
stocked twice a year.
141

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Table 1. Characteristics of North Twins Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Cobbly, Gravelly, and Stony
Loams.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Bluebunch Wheatgrass
Unknown
Unknown
142

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Table 2. Characteristics of North Twins Lake.
elevation (ft.)
5,171.00
surface area (acres)
14.27
volume (acre-ft.)
Unknown
maximum depth (ft.)
8.0
mean depth (ft.)
unknown
shoreline length (ft.)
4,217.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
143

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Table 3. Major ions and related water quality variables for North
Twins Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 11 August 1993.
~TW2	1993
Mean	Mean
pH (range) 	
8.
87
alkalinity (mg/L CaCo3) 	
257.40
conductivity (umhos/cm) 	
459.00
turbidity (NTU) 	
1.
80
dissolved oxygen 	
8.
10
total suspended solids 	
1.
01
Ca 	
18
.94
Mg 	
51
.06
K 	
2.
25
Na 	
17
.75
CI 	
2.
32
S04 	
12
.67
144

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Table 4. Nutrient, chlorophyll a and Secchi depth data for North
Twins Lake. Average concentrations in ug/L. A sample was
collected from the euphotic zone on 11 August 1993.
1992	1993
Mean	Mean
12.7
5.30
< 2
1.59
8'3"
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
145

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South Twins Lake
South Twins Lake is positioned twenty miles south of
Browning on BIA Highway 1 and five miles north west of Heart
Butte on the same highway. South Twins is set immediately below
the Rocky Mountains on its foothills.
This lake has a limited number of tables and fireplaces
about its shoreline which the Blackfeet Fish & Game monitors
quite actively. Tribal land surrounds this lake. There are
several residents which occupy a radius of 3-5 miles around the
lake.
South Twins is a very popular fishing lake year around.
This lake is one of the smallest sports fishing lakes which hosts
numerous derbies. Also, recreational functions are popular
during the summer months. They include picnicking, camping,
swimming, etc.
Drainage Basin Characteristics
South Twins Lake sits in the south central portion of the
Two Medicine drainage basin. This lake is charged by ground
water and run off. There is one tributary which flows into South
Twins Lake from the south side. This water comes from Evans
Creek. There is a culvert on the north side of lake which
releases excess water out of South Twins.
South Twins Lake is situated in the Montana Valley and
Foothill Prairies Ecoregion. The bluebunch wheatgrass is the
main vegetational species under normal conditions. The riparian
soils are comprised of cobbly, gravelly, and stony loams.
The drainage basin consists of mountains and forest to the
south and west, and range changing to farm land the further east
you venture.
Lake Basin Characteristics
The deepest point measured was fifteen feet near the center
of the lake. Twins South Lake has a comparative small surface
area of 22.17 acres. The shoreline length was measured at 3,792
feet. Willows dominant the south shore while grassy type
vegetation covers the remainder of the lake.
South Twins Lake has an elevation of 5,171 feet. The volume
of water is controlled by turnout on north side of lake.
146

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Water Quality
The earlier monitoring, of South Twins Lake, occurred in 1966
and 1967 and this data was placed in the 208 Water Quality
Management Plan of the Blackfeet Tribe. Monitoring was
revitalized in 1993 by the Blackfeet Environmental Office through
the Clean Lakes Program.
The moderately low concentrations of calcium and magnesium
signify that the water is slightly hard. The lake is well
buffered by looking at the value of alkalinity.
Analyzing limited data, South Twins Lake would fall under
the classification of oligotrophic because of low concentrations
of nutrients, low chlorophyll a value, high secchi reading, lack
of algae, and the clearness of the water.
Biological Characteristics
Fish:
Because South Twins Lake is heavily fished, it is stocked
biannually with rainbow trout.
147

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Table 1. Characteristics of South Twins Lake drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Cobbly, Gravelly, and Stony
Loams.
Unavailable
Unavailable
Montana Valley and Foothill
Prairies
Bluebunch Wheatgrass
Unknown
Unknown
148

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Table 2. Characteristics of South Twins Lake.
elevation (ft.)
5,171.00
surface area (acres)
22.17
volume (acre-ft.)
Unknown
maximum depth (ft.)
15.0
mean depth (ft.)
unknown
shoreline length (ft.)
3,792.00
mean annual lake evaporation (in.)
Unknown
mean annual precipation (in.)
15-19"
mean residence time (yr.)
Not available
control structure
None
149

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Table 3. Major ions and related water quality variables for South
Twins Lake. Average concentrations in mg/L; pH in pH units. A
sample was collected from euphotic zone on 11 August 1993.
1992
1993
Mean
Mean
pH (range) 	
8.33
alkalinity (mg/L CaCo3) 	
224.40
conductivity (umhos/cm) 	
410.00
turbidity (NTU) 	
1.48
dissolved oxygen 	
7.20
total suspended solids 	
1.90
Ca 	
33.25
Mg 	
33.09
K 	
1.66
Na 	
11.24
CI 	
2.51
S04 	
11.19
150

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Table 4. Nutrient, chlorophyll a and Secchi depth data for South
Twins Lake. Average concentrations in ug/L. A sample was
collected from the euphotic zone on 11 August 1993.
1992	1993
Mean	Mean
14.5
7.48
< 2
2.14
10' 5 "
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
151

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Lower Two Medicine
Lower Two Medicine Lake is a man made water resource. The
current dam was built in 1966 after the flood destroyed the
former dam in 1964. Lower Two Medicine is engraved into the
picturesque view of the Rocky Mountains. The lake lies four
miles to north of the community of East Glacier on Highway 49.
The shoreline encompassing the lake is tribally owned, and
is partially accessible from the east and west sides. There are
no dwellings around the lake, but there is a conveince store
located a quarter of a mile below the dam. A campground is
situated around the store and part way up the western end of the
lake.
In the summer months, Lower Two Medicine is used by
recreational seekers in the form of swimming, boating, water
skiing, picnicking, fishing, etc. The lake provides fishing year
around.
Drainage Basin Characteristics
Lower Two Medicine Lake is found in the north western
section of the Two Medicine drainage basin. The western end of
Two Medicine Lake lies within Glacier National Park. This
drainage basin had the most acre-feet of water leaving the
reservation in 1991 than the other three basins. The natural
drainage has been altered by Two Medicine Dam. Lower Two
Medicine is charged by run off, ground water, and one major
tributary. Two Medicine river enters the lake from the west end
and is responsible for the largest contribution of water to this
lake. On the southeast end of lake, water leaves Two Medicine
Lake via a dam. The water exiting Two Medicine Lake eventually
is deposited into the Marias River to the east.
Lower Two Medicine lake exists in the Northern Rockies
Ecoregion. The riparian soils embedded along this lake are
composed of various types of loams. In these soils, Lodgepole
pine, Englemann spruce, Douglas fir , Alpine fir, and Aspen are
the dominant vegetation.
The drainage basin is overlaid with forest and mountains to
the west, and valley/prairies to the east. Ranching tends to be
conjugated more in the western half of the basin with farming
becoming more prominent towards the eastern side.
152

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Lake Basin Characteristics
Lower Two Medicine Lake is a fairly deep mountainous lake
with 49 feet being the deepest point measured in 1993. This lake
has a surface area of 716.70 acres with a shoreline length of
38,2545 feet. This shoreline is very long with thick timber
stands encircling the lake.
Lower Two Medicine has an elevation of 4,882 feet. The
water level, of this lake, is manipulated by a dam on southeast
end. The purpose of this dam is for flood control and to release
water for irrigational uses.
Livestock use Lower Two Medicine as a drinking source and
graze on land near it.
Water Quality
Lower Two Medicine was partially monitored in 1963-64 with
the results placed in the 1981 Water Quality Management Plan of
the Blackfeet Tribe. This lake was more intensely monitored by
the Blackfeet Environmental Office in 1993.
Lower Two Medicine is a freshwater lake with total suspended
solids and alkalinity concentrations being the one of the lowest
on the reservation. The water is considered soft because the
calcium and magnesium levels are quit low.
At this time, Lower Two Medicine Lake would be classified as
an oligotrophic lake because the nutrient values are very low,
Chlorophyll a values are < 1, and secchi readings are moderately
high (Table 3). Further testing would have to be done to verify
the trophic status of this lake.
Biological Characteristics
Fish:
Lower Two Medicine Lake contains the rainbow trout, brook
trout, and the white suckers in its pristine waters.
153

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Table 1. Characteristics of Lower Two Medicine drainage basin.
area(excluding lake) (miles sq.)
soil
berock geology
terrain
ecoregion
dominant vegetation
mean annual inflow (acres-ft)
mean annual sunshine
Unavailable
Stony, Gravelly, Cobbly,
Cobbly Clay, and Gravelly
Clay Loams.
Unavailable
Unavailable
Northern Rockies
Alpine Fir, Aspen, Douglas
Fir, Englemann Spruce,
Lodgepole Pine.
Unknown
Unknown
154

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Table 2. Characteristics of Lower Two Medicine Lake.
elevation (ft.)
surface area (acres)
maximum storage (acre-ft.)
normal storage (acre-ft.)
maximum depth (ft.)
mean depth (ft.)
shoreline length (ft.)
control structures
dam height (ft.)
dam crest length (ft.)
dam crest elevation (ft.)
overflow spillway crest
elevation (ft.)
mean annual lake evaporation (in.)
mean annual precipation (in.)
mean residence time (yr.)
4,882.00
716.70
25,100.00
11,850.00
49.0
unknown
38,254.00
earth dam with concrete
overflow structure
65.0
1100.00
4,883.00
4,883.00
Unknown
20" +
Not available
155

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Table 3. Major ions and related water quality variables for Lower
Two Medicine Lake. Average concentrations in mg/L; pH in pH
units. Samples were collected from euphotic zone once on 3 August
1993. There were four grab samples collected at this visit.
1992
1993
Mean
Mean
pH (range) 	
7.18
alkalinity (mg/L CaCo3) 	
24.20
conductivity (umhos/cm) 	
103.00
turbidity (NTU) 	
1.35
dissolved oxygen 	
6.25
total suspended solids 	
< 0.5
Ca 	
8.51
Mg 	
4.29
K 	
0.24
Na 	
0.51
CI 	
0.15
S04 	
2.73
156

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Table 4. Nutrient, chlorophyll a and Secchi depth data £or Lower
Two Medicine Lake. Average concentrations in ug/L. Samples were
collected from the euphotic zone once on 3 August 1993. There
were four grab samples collected at this visit.
1992	1993
Mean	Mean
6.80
9.66
<2
0.476
7'8"
total phosphorus
NH3-N
N02/3
chlorophyll a
secchi depth (ft)
157

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