U.S. ENVIRONMENTAL PROTECTION AGENCY
            NATIONAL EUTROPHICATION SURVEY
                      WORKING PAPER SERIES
        PACIFIC NORTHWEST ENVIRONMENTAL RESEARCH LABORATORY
                      An Associate Laboratory of the
          NATIONAL ENVIRONMENTAL RESEARCH CENTER - CORVALLIS, OREGON
                              and
     NATIONAL ENVIRONMENTAL RESEARCH CENTER - LAS VEGAS, NEVADA
	697.032

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                                    905R75010
                                    REPORT
                                      ON
                                   DERLAKE
                               MARQUOTE COUN1Y
                                   MICHIGAN
                                 EPA REGION V
                             WORKING PAPER No,  192
       WITH THE COOPERATION OF THE
MICHIGAN DEPARTMENT OF NATURAL RESOURCES
                 AND THE
         MICHIGAN NATIONAL GUARD
             FEBRUARY, 1975
                             U.S. Environmental Protection Agency
                             Region 5, Library (PH2J)
                             77 Wtst Jackson Boulevard, 12th Roar
                             Chicago. 11  60604-3590

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                               CONTENTS
                                                           Page
  Foreword                                                  i i
  List of Michigan Study Lakes                               iv
  Lake and Drainage Area Map                                 v

  Sections
  I.   Conclusions                                             1
 II.   Lake and Drainage Basin  Characteristics                 4
III.   Lake Water Quality Summary                             5
 IV.   Nutrient Loadings                                      8
  V.   Literature Reviewed                                   13
 VI.   Appendices                                            14

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                                11
                         FOREWORD
    The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophication to fresh water lakes and
reservoirs.

OBJECTIVES

    The Survey was designed to develop, in conjunction with state
environmental agencies, information on nutrient sources, concentrations,
and impact on selected freshwater lakes as a basis for formulating
comprehensive and coordinated national, regional, and state management
practices relating to point-source discharge reduction and non-point
source pollution abatement in lake watersheds.

ANALYTIC APPROACH

    The mathematical and statistical procedures selected for the
Survey's eutrophication analysis are based on related concepts that:

        a.  A generalized representation or model relating
    sources, concentrations, and impacts can be constructed.

        b.  By applying measurements of relevant parameters
    associated with lake degradation, the generalized model
    can be transformed into an operational representation of
    a lake, its drainage basin, and related nutrients.

        c.  With such a transformation, an assessment of the
    potential for eutrophication control can be made.

LAKE ANALYSIS

    In this report, the first stage of evaluation of lake and water-
shed data collected from the study lake and its drainage basin is
documented.  The report is formatted to provide state environmental
agencies with specific information for basin planning [§303(e)], water
quality criteria/standards review [§303(c)], clean lakes [§314(a,b)],
and water quality monitoring [§106 and §305(b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.

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                                Ill
    Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic condi-
tion are being made to advance the rationale and data base for
refinement of nutrient water quality criteria for the Nation's
fresh water lakes.  Likewise, multivariate evaluations for the
relationships between land use, nutrient export, and trophic
condition, by lake class or use, are being developed to assist
in the formulation of planning guidelines and policies by EPA
and to augment plans implementation by the states.

ACKNOWLEDGMENT

    The staff of the National Eutrophication Survey (Office of
Research & Development, U. S. Environmental Protection Agency)
expresses sincere appreciation to the Michigan Department of
Natural Resources for professional involvement and to the
Michigan National Guard for conducting the tributary sampling
phase of the Survey.

    A. Gene Gazlay, former Director, and David H. Jenkins, Acting
Director, Michigan Department of Natural Resources; and Carlos
Fetterolf, Chief Environmental Scientist, and Dennis Tierney,
Aquatic Biologist, Bureau of Water Management, Department of Natural
Resources, provided invaluable lake documentation and counsel during
the course of the Survey.  John Vogt, Chief of the Bureau of Environ-
mental Health, Michigan Department of Public Health, and his staff
were most helpful in identfying point sources and soliciting municipal
participation in the Survey.

    Major General Clarence A. Schnipke (Retired), then the Adjutant
General of Michigan, and Project Officer Colonel Albert W. Lesky,
who directed the volunteer efforts of the Michigan National Guardsmen,
are also gratefully acknowledged for their assistance to the Survey.

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                                IV
                  NATIONAL EUTROPHICATION SURVEY

                            STUDY LAKES
                         STATE OF MICHIGAN
LAKE NAME

Allegan Res.
Barton
Belleville
Betsie
Brighton
Caro Res.
Charlevoix
Chemung
Constantine Res,
Crystal
Deer
Ford
Fremont
Higgins
Hoi 1oway Res.
Houghton
Jordon
Kent
Long
Macatawa
Manistee
Nona
Muskegon
Pentwater
Pere Marquette
Portage
Randall
Rogers Pond
Ross
St. Louis Res.
Sanford
Strawberry
Thompson
Thornapple
Union
Whi te
COUNTY

Allegan
Kalamazoo
Wayne
Benzie
Livingston
Tuscola
Charlevoix
Livingston
St. Joseph
Montcalm
Marquette
Washtenaw
Newago
Roscommon
Genesee, Lapeer
Roscommon
Ionia, Barry
Oakland
St. Joseph
Ottawa
Manistee
Muskegon
Muskegon
Oceana
Mason
Houghton
Branch
Mecosta
Gladwin
Gratiot
Midland
Livingston
Livingston
Barry
Branch
Muskegon

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                             DEER LAKE
                          STORE! NO. 2624

    CONCLUSIONS
    A.  Trophic Condition:
            Deer Lake was sampled only two times.  On the basis of
        these somewhat limited data, it appears that the lake is eu-
        trophic.  Of the 35 Michigan lakes on which sampling was
        completed, 31 had less mean total and dissolved phosphorus,
        16 had greater Secchi disc transparency, and 25 had less mean
        chlorophyll  a*.
            Survey limnologists noted heavy algal growths in many por-
        tions of the lake.
    B.  Rate-Limiting Nutrient:
            An algal assay sample was not taken at Deer Lake.  However,
        the lake data indicate nitrogen limitation in June and September
        (i.e., N/P ratios were 3/1 or less).
    C.  Nutrient Controllability:
            1.  Point sources--During the sampling year, Deer Lake
        received a total phosphorus load at a rate nearly four times
        that proposed by Vollenweider (in press) as "dangerous"; i.e.,
        a eutrophic rate (see page 12).  Now, Vollenweider's model may
        not apply to water bodies with short hydraulic retention times,
* See Appendix A.

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and the hydraulic retention time of Deer Lake is  not known.
However, the maximum depth sounded by Survey limnologists
was 24 feet; and, if it is assumed that the mean  depth is
about one-third of that (i.e., eight feet), the mean hydraulic
retention time would be about 90 days.  If the assumed mean
depth is reasonable, Vollenweider's model  may be  applicable
to Deer Lake, although it is noted that less than 9% of the
total phosphorus load was retained in the lake which indicates
a rather short retention time.
    It is calculated that the wastewater treatment plants
serving Ishpeming and Ishpeming Township contributed nearly
85% of the total phosphorus load to Deer Lake during the
sampling year.  Removal of 80% of the phosphorus  at these
                                                 2
sources would reduce the loading rate to 0.76 g/m /yr or
about 1.2 times the eutrophic rate.  In view of the ques-
tionable applicability of Vollenweider's model, it is likely
that the reduced loading would improve the trophic condition
of the lake and, in particular, reduce the incidence and sever-
ity of nuisance algal blooms as well as provide additional
protection for downstream Lake Superior.
    2.  Non-point sources (see page 12)--During the sampling
year, the phosphorus export of Gold Mine Creek was a rather

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               2
high TOO Ibs/mi /yr.  The relatively high Carp Creek export
may have been due to underestimation of the phosphorus load
from the Ishpeming Township B plant.
    In all, it is estimated that non-point sources,  including
precipitation, contributed only about 15% of the total phos-
phorus load to Deer Lake during the sampling year.

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II.   LAKE AND DRAINAGE  BASIN  CHARACTERISTICS
     A.   Lake Morphometry :
         1.   Surface  area:  897  acres.
         2.   Mean  depth:   unknown.
         3.   Maximum  depth:   >20 feet.
         4.   Volume:  unknown.
     B.   Tributary and  Outlet:
         (See Appendix  B  for  flow data)
         1.   Tributaries  -
             Name                               Drainage  area*  Mean  flow*
             Carp  Creek                          24.0 mi2       28.2 cfs
             Gold  Mine  Creek                       4.9 mi         6.0 cfs
             Minor tributaries &                        2
              immediate drainage -                6.0 mi         6.2 cfs
                          Totals                 34.9 mi2       40.4 cfs
         2.   Outlet -
             Carp  River                          36.3 mi **    40.4 cfs
     C.   Precipitation***:
         1.   Year  of  sampling:   37.9 inches.
         2.   Mean  annual:  32.0  inches.
 t Miller and Thompson,  1970.
 * Drainage areas are accurate within ±5%;  mean daily flows  for 74% of the
   sampling sites are accurate within ±25%  and the remaining sites  up  to
   ±40%; and mean monthly flows,  normalized mean monthly flows, and mean
   annual flows are slightly more accurate  than mean daily flows.
 ** Includes area of lake.
 *** See Working Paper No. 1,  "Survey Methods, 1972".

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III.   LAKE WATER QUALITY  SUMMARY
      Deer Lake was  sampled twice  during  the  open-water season  of 1972
  by  means of a pontoon-equipped Huey  helicopter.   Each time, samples
  for physical  and chemical  parameters were collected  from  four stations
  on  the lake and from a  number of depths at  each  station  (see  map,  page
  v).  During each visit,  a single depth-integrated (near bottom to  sur-
  face)  sample was composited  from the stations  for phytoplankton identi-
  fication and enumeration,  and a  similar sample was collected  for chloro-
  phyll  ^analysis.   The  maximum depths sampled  were 13 feet at station 1,
  16  feet at station 2, 16 feet at station 3,  and  20 feet at station 4.
      The results obtained are presented  in full in Appendix C, and  the
  data for the September  sampling  period  when  the  lake essentially was
  well-mixed, are summarized below.  Note, however, the Secchi  disc  sum-
  mary is based on all  values.
      For differences in  the various parameters  in June, refer  to Appendix
  C.

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A.  Physical and chemical characteristics:
    Parameter               Minimum

    Temperature (Cent.)      16.9
    Dissolved oxygen (mg/1)   6.4
    Conductivity (ymhos)    220
    pH (units)                8.2
    Alkalinity (mg/1)        52
    Total P (mg/1)            0.231
    Dissolved P (mg/1)        0.203
    N0? + NO. (mg/1)          0.030
    Amfflonia fmg/1)            0.060
              FALL VALUES

              (09/10/72)

             Mean       Median
                     Maximum
17.3
8.0
228
8.4
56
0.255
0.219
0.038
0.082
17.4
7.8
225
8.4
54
0.249
0.218
0.040
0.070
17.6
9.4
240
8.6
63
0.282
0.243
0.050
0.170
                                           ALL VALUES
    Secchi disc (inches)
36
58
72
72

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B.  Biological  characteristics:

    1.  Phytoplankton -
        Sampling
        Date

        06/24/72
        09/10/72
Dominant
Genera
1.
2.
3.
4.
5.


1.
2.
3.
4.
5.

Fragilaria
Polycystis
Cyclotella
Cryptomonas
Anabaena
Other genera
Total
Microcystis
Melosira
Dinobryon
Cyclotella
Flagellates
Other genera
                                          Total
                                                 Number
                                                 per ml

                                                 4,955
                                                   362
                                                   344
                                                   127
                                                    90
                                                   270

                                                 6,148

                                                   226
                                                   206
                                                   186
                                                   116
                                                   105
                                                   467

                                                 1,306
    2.
Chlorophyll  a^ -
(Because of instrumentation problems during the 1972 sampling,
the following values may be in error by plus or minus 20 percent.)
        Sampling
        Date

        06/24/72
        09/10/72
                     Station
                     Number

                       01
                       02
                       03
                       04

                       01
                       02
                       03
                       04
Chlorophyll  a,
(ug/D

    66.1
    42.8
    44.8
    18.3

     4.0
     1.8
     2.3
     1.1

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IV.   NUTRIENT LOADINGS
     (See Appendix D for data)
     For the determination  of nutrient  loadings,  the Michigan  National
 Guard collected monthly near-surface grab  samples  from each of the tribu-
 tary sites  indicated on the map  (page  v),  except for  the months of May
 and September when two  samples were collected.   Sampling was  begun in
 October, 1972,  and was  completed  in September, 1973.
     Through an interagency agreement,  stream  flow  estimates for the year
 of  sampling and a "normalized" or average  year were provided  by the Michi-
 gan District Office of  the U.S. Geological  Survey  for the  tributary sites
 nearest the lake.
     In this report, nutrient loads for sampled tributaries were deter-
 mined by using a modification of  a U.S.  Geological Survey  computer
 program for calculating stream loadings*.   Nutrient loadings  for  unsam-
 pled "minor tributaries and immediate  drainage"  ("ZZ" of U.S.G.S.) were
 estimated by using the  means of the nutrient  loads, in Ibs/mi^/year,  in
 Gold Mine Creek at station C-l and multiplying the means by the ZZ area
 in  mi .
     The operators of the Ishpeming and the Ishpeming  Township A wastewater
 treatment plants provided  monthly effluent samples and corresponding  flow
 data.  However, the Ishpeming Township B plant was not sampled, and nutrient
 loads were  estimated at 2.5 Ibs  P and  7.5  Ibs N/capita/year.
 * See Working Paper No.  1.

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    A.  Waste Sources:

        1.  Known municipal* -
Name
Ishpeming
Ishpeming
Township A
Ishpeming
Township B
Pop.
Served
8,000
1,550
400
Treatment
Prim.
clarifier
Imhoff tank
Imhoff tank
Mean
Flow (mgd)
1.848
0.129
0.040**
Receiving
Water
Carp River
Carp River
Carp River
        2.  Known industrial - None
* Erickson, 1973.
** Estimated at 100 gal/capita/day.

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                                 10
    B.   Annual  Total  Phosphorus  Loading  - Average  Year:
        1.   Inputs  -
                                              Ibs  P/          %  of
            Source                             yr             total
            a.   Tributaries  (non-point load)  -
                Carp  Creek                     2,410          12.8
                Gold  Mine Creek                   160            0.8
            b.   Minor tributaries  & immediate
                 drainage (non-point load) -      200            1.1
            c.   Known municipal  STP's -
                Ishpeming                     11,300          59.9
                Ishpeming Township A           3,660          19.4
                Ishpeming Township B           1,000            5.3
            d.   Septic tanks  - unknown
            e.   Known industrial  - none
            f.   Direct precipitation* -           140            0.7
                         Total                18,870          100.0
        2.   Outputs -
            Lake outlet - Carp River          17,240
        3.   Net annual P accumulation -  1,630 pounds
* See Working Paper No. 1.

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                                 11
    C.  Annual Total Nitrogen Loading - Average Year:
        1.  Inputs -
                                              Ibs N/         % of
            Source                            yr	         total
            a.  Tributaries (non-point load) -
                Carp Creek                     84,640         43.6
                Gold Mine Creek                14,180          7.3
            b.  Minor tributaries & immediate
                 drainage (non-point load) -   17,360          9.0
            c.  Known municipal STP's -
                Ishpeming                      51,670         26.6
                Ishpeming Township A           14,420          7.4
                Ishpeming Township B            3,000          1.6
            d.  Septic tanks - unknown
            e.  Known industrial - none
            f.  Direct precipitation* -         8,640          4.5
                         Total                193,910        100.0
        2.  Outputs -
            Lake outlet - Carp River          146,930
        3.  Net annual N accumulation  - 46,980 pounds
* See Working Paper No. 1

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                             12
D.  Mean Annual  Non-point Nutrient Export by Subdrainage Area:

    Tri butary                             Ibs P/mi2/yr   Ibs N/mi2/yr

    Carp Creek                                 100          3,527
    Gold Mine Creek                             33          2,894

E.  Yearly Loading Rates:

        In the following table, the existing phosphorus loading

    rates are compared to those proposed by Vollenweider (in press).

    Essentially, his "dangerous" rate is the rate at which the

    receiving water would become eutrophic or remain eutrophic;

    his "permissible" rate is that which would result in the

    receiving water remaining oligotrophic or becoming oligotrophic

    if morphometry permitted.  A mesotrophic rate would be consid-

    ered one between "dangerous" and "permissible".

        Note that Vollenweider's model  may not be applicable to

    water bodies with very short hydraulic retention times.

                               Total  Phosphorus       Total Nitrogen
    Units	Total   Accumulated    Total    Accumulated

    Ibs/acre/yr               21.0       1.8         216.2        52.4
    grams/m2/yr                2.36      0.20         24.2         5.9
    Vollenweider loading rates for phosphorus
     (g/m^/yr)  based on surface area and mean
     outflow of Deer Lake:

        "Dangerous"  (eutrophic rate)       0.62
        "Permissible"  (oligotrophic rate)  0.31

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                                 13
V.  LITERATURE REVIEWED

    Erickson,  John,  1973.   Treatment plant questionnaire  (Ishpeming  and
        Ishpeming Township treatment plants).   MI  Dept. of Publ.  Health,
        Escanaba.

    Miller, J. B., and T.  Thompson,  1970.   Compilation of data  for Michigan
        lakes.  U.S.  Geol. Survey,  Dept.  Interior, and MI  Dept. of Nat.
        Resources, Lansing.

    Vollenweider, Richard  A.  (in press).   Input-output models.  Schweiz
        Z.  Hydro!.

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VI.  APPENDICES
                            APPENDIX A
                           LAKE RANKINGS

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     APPENDIX B
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-------
       APPENDIX D
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