Mn 17 Fact Sheet

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    Assessment Point: MN-17

    The following data are excerpts from multiple reports. While the same locationMenomonee River watershed is represented, the assessment point IDs differ. Th

    the following data, Assessment Point MN-17 is also represented by:

    o Reach 908o North 70th Streeto RI-09o Menomonee River Downstream of Honey Creek

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    94

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    tu41C i t y o f C i t y o f

    B R O O K F I E L D B R O O K F I E L D

    City ofCity of

    CED A RBUR GCE DA RBURG

    C it y ofC i t y o f

    WAU WA TOS AWAU WAT OS A

    C it y ofC i t y o f

    ME QUO NM EQ UO N

    UPPER MENOMONEE RIVER

    LOWER MENOMONEE RIVER

    LITTLEMENOMONEERIVER

    UNDERWOOD CREEK

    LILLY CREEK

    WILLOWCREEK

    BUTLER DITCH

    NOR-X-WAY CHANNEL

    DOUSMAN DITCH

    WEST BRANCH MENOMONEERIVER

    NORTH BRANCH MENOMONEE RIVER

    LITTLE MENOMONEE CREEK

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    LILLY

    DIT

    CH

    PIGEON

    NOR

    -X-WAY

    SUS

    SEX

    DOUSMAN

    UNDER

    WOOD

    CREEK

    CRE

    EK

    CREEK

    RIVER

    CREE

    K

    CR

    EEK

    LITTLE

    MENOMONEE

    MENOMONEE

    RIVER

    MENOM

    ONEE

    LINC

    BARK

    W.

    CREEK

    CHANNEL

    AMY

    BELL

    LAKE

    MENOMONEE

    PEWA

    UKEE

    RIVER

    BARK

    RIVER

    MENOMON

    EE

    RIV

    ER

    BR.

    WILLOW

    RIVER

    FOX

    LAKE

    MENOMONEE

    MENOM

    ON

    EE

    LITTL

    E

    RIV

    ER

    BR.

    RI

    VER

    RIVER

    N.

    C i t y o f C i t y o f

    B R O O K F I E L D B R O O K F I E L D

    C i t y o f C i t y o f

    M E Q U O N M E Q U O N

    C i t y C i t y

    MI L W AMI L W A U

    Ci ty o fCi ty o f

    W A UWA T O SAWA UWA TOSA

    UPPER MENOMONEE RIVER

    LOWER MENOMONEE RIVER

    LITTLEMENOMONEERIVER

    UNDERWOOD CREEK

    LILLY CREEK

    WILLOWCREEK

    BUTLER DITCH

    NOR-X-WAY CHANNEL

    DOUSMAN DITCH

    WEST BRANCH MENOMONEERIVER

    NORTH BRANCH MENOMONEE RIVER

    LITTLE MENOMONEE CREEK

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    !

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    !

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    !

    !

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    !

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    !!

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    !!!

    94

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    tu41C i t y o f C i t y o f

    B R O O K F I E L D B R O O K F I E L D

    C i t y o f C i t y o f

    M E Q U O N M E Q U O N

    C i t y C i t y

    MI L W AM I L W A U

    Ci ty o fCi ty o f

    W A UWA T O SAWA UWA TOSA

    MN-11

    MN-9

    MN-14

    MN-2

    MN-5

    MN-15

    MN-13

    MN-4

    MN-7

    MN-8

    MN-3

    MN-6

    MN-1

    MN-10

    MN-17

    MN-12

    MN-8MN-9

    MN-7

    MN-6

    MN-5

    MN-4

    MN-3 MN-2

    MN-1

    MN-16 MN-17

    MN-15

    MN-14

    MN-13

    MN-11

    MN-12

    MN-10

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    !

    !

    !

    !

    M

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    !

    !

    !

    !

    City ofCity of

    WA UWA TOSAWA UWA TOSA

    Bluemound

    76th

    M

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    Constituent Measure Standard/Ta

    Variance Standard - Geomean not to exceed 1,000 counts/

    Variance Standard - Less than 10% of all samples/month 2,000 counts/

    Dissolved Oxygen (DO) Variance Standard - Minimum Concentration 2 mg/l

    Total Suspended Solids (TSS)

    USGS Median TSS Reference Concentration (estimated

    background concentration) 17.2 mg/l

    Total Phosphorus (TP) Planning Guideline 0.1 mg/l

    Flashiness

    Richards Baker Flashiness Index (quantifies the frequencyand rapidity of short-term changes in stream flow; the index

    ranges from 0 - 2, with 0 being constant flow) indicator only

    Menomonee River - Variance Standards/Targets

    Fecal Coliform

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    Figure Overall Project

    Team Assessment

    A

    Chloride by flow(Cl not from

    models)

    Inconclusive (nowinter data)

    It is difficult to assess chloride trends without data from thbeing actively applied, some amount is in a reservoir (se

    noticeable during mid-to-dry conditions. During higher fl

    Dissolved oxygen

    by flow

    Good Note that the decline in dissolved oxygen occurs at low flagitation and higher temperatures (low flow conditions ar

    Fecal coliform by

    flow

    Moderate to Poor Generally, a pollutant that is present at high concentration(fecal coliform, in this case) is attributed primarily to non

    years) would only contribute during the high flows when

    any period with the highest flows, fecal coliform counts e

    exceed the variance standard over 50% of the time. Durinwould be the safest time for any recreational uses (boating

    Phosphorus by

    flow

    Moderate to Poor Concentrations of phosphorus are greatest at high and lowparticularly noticeable at low flows (perhaps from non-co

    at high flows.

    Suspended solids

    by flow

    Good The concentrations of suspended solids increase with incrThe suspended solids may come from runoff that carries a

    stream sediments.

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    Flashiness Index

    Reach Description Richards Baker Flashiness Index

    RI-09 North 70th

    Street 0.49

    Flashiness Index

    North 70th Street (908)

    0

    200

    400

    600

    800

    1000

    1200

    Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

    AVERA

    GEDAILYFLOW(CF

    S

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    Existing Water Quality Data

    AssessmentPoint

    Water QualityIndicator

    Statistic CondExis

    Mean (cells per 100 ml) 6,9Fecal Coliform Bacteria(annual)

    Percent compliance with single samplestandard (

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    0

    40

    80

    120

    160

    200

    240

    280

    320

    360

    400

    0-1

    1-2

    2-3

    3-4

    4-5

    5-6

    6-7

    Average DO (mg/L)

    AverageNu

    mberofDaysPerYear

    Menomonee River @ N. 70th Street (RI 09)

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    Menomonee River @ N. 70th Street (RI

    0

    40

    80

    120

    160

    200

    240

    280

    320

    360

    400

    0-400

    400-600

    600-1000

    1000-2000

    2000-3000

    Average Fecal Coliform (#/100ml)

    AverageNumberofDaysPerYear

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    Menomonee River @ N. 70th Street (R

    0

    40

    80

    120

    160

    200

    240

    280

    320

    360

    400

    0-0.05

    0.05-0.1

    0.1-0.15

    0.15-0.2

    0.2-0.25

    0.25-0.3

    0.3-0.35

    Average TP (mg/L)

    AverageNumberofDaysPerYear

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    Menomonee River @ N. 70th Street (R

    0

    40

    80

    120

    160

    200

    240

    280

    320

    360

    400

    0-25

    25-50

    50-75

    75-100

    100-125

    125-150

    Average TSS (mg/L)

    AverageN

    umberofDaysPerYear

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    1

    10

    100

    1000

    0 10 20 30 40 50 6

    Flow Duration Interval (%

    Concentra

    tion(mg/L)

    Flow Conditions Acute Toxicity (757 mg/L) Chronic Toxicity (39

    North 70th Street (RI-09) RChloride

    Modeled Flow Data; Chloride Field Data

    Mid-rangeFlows

    HighFlows

    MoistConditions

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    1

    10

    100

    0 10 20 30 40 50 60

    Flow Duration Interval (%)

    Concentra

    tion(mg/L)

    Flow Conditions Special Variance Regulatory Standard (2 mg/L)

    North 70th Street (RI-09) RDissolved Oxygen

    Modeled Flow Data

    Mid-rangeFlows

    HighFlows

    MoistConditions

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    1.E+00

    1.E+01

    1.E+02

    1.E+03

    1.E+04

    1.E+05

    0 10 20 30 40 50

    Flow Duration Interval (%

    C

    oncentratio

    n(

    cfu/100mL)

    Flow Conditions Regulatory Standard- Special Variance (2,000 cfu/1

    North 70th Street (RI-09) RFecal Coliform

    Modeled Flow Data

    Mid-rangeFlows

    High

    Flows

    Moist

    Conditions

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    0.01

    0.10

    1.00

    0 10 20 30 40 50 6

    Flow Duration Interval (%)

    Concentra

    tion(mg/L)

    Flow Conditions Planning Standard (0.1 mg/L)

    North 70th Street (RI-09) RTotal Phosphorus

    Modeled Flow Data

    Mid-rangeFlows

    HighFlows

    MoistConditions

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    1

    10

    100

    1000

    0 10 20 30 40 50 6

    Flow Duration Interval (%

    Concentration(mg/L)

    Flow Conditions Reference Concentration (17.2 mg/L)

    North 70th Street (RI-09) RTotal Suspended Solid

    Modeled Flow Data

    Mid-rangeFlows

    HighFlows

    MoistConditions

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