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    94

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    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 C E D A R B UR G C E D A R B U R G

    C it y of C it y o f W AU W A T OS AW AU W AT OS A

    C it y of Ci t y of ME Q UO N M EQ UO N

    UPPER MENOMONEE RIVER

    LOW E R MENOMONEE RIV E R

    LI T TLE MENO M O N E E RIVER

    UNDERWOOD CREEK

    LILLY CREEK

    WILLO W C R E EK

    BUTLER DITCH

    NOR-X-WAY CHANNEL

    DOUSMAN DITCH

    WEST BR A NCH MENOMO N E E RIV E R

    NORTH BRANCH MENOMONEE RIVER

    LITTLE MENOMONEE CREEK

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    94

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    L I L L Y

    D I T C H

    P I G E O N

    N O R - X - W A Y

    S U S S E X

    DO USMAN

    U N D

    E R W O O D

    C R E E K

    C R E E K

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    E E K

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    C R E E K

    C R E E K

    L I T T L E

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    M E N O M

    O N

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    C R E E K

    C H A N

    N E L

    AMY BELL LAKE

    M E N O M O N E E

    P E W A

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    M E N O M O N E E

    M E N O M

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    R I V E R

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    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

    M I L W A UM I L W A U

    C i t y o f C i t y o f W A U W A T O S AW A U W A T O S A

    UPPER MENOMONEE RIVER

    LOW E R MENOMONEE RIV E R

    LI T TL E MENO M O N E E RIVER

    UNDERWOOD CREEK

    LILLY CREEK

    WILLO W C R E EK

    BUTLER DITCH

    NOR-X-WAY CHANNEL

    DOUSMAN DITCH

    WEST BR A NCH MENOMO N E E RIV E R

    NORTH BRANCH MENOMONEE RIVER

    LITTLE MENOMONEE CREEK

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    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

    M I L W A UM I L W A U

    C i t y o f C i t y o f W A U W A T O S AW A U W A T O S A

    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-8 MN-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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    !

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    Me q u o n R

    A p p l e t o n A v .

    M i St

    MN-5

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    !

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    Me q u o n R

    A p p l e t o n A v .

    M i St

    MN-5

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    Constituent Measure Standard/Target

    Geometric Mean Standard 200 counts/100

    Not to Exceed Standard 400 counts/100

    Dissolved Oxygen (DO) Minimum Concentration Standard 5 mg/l

    Total Suspended Solids (TSS)USGS Median TSS Reference Concentration (estimatedbackground 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 indexranges from 0 - 2, with 0 being constant flow) indicator only

    Menomonee River Standards/Targets

    Fecal Coliform

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    Figure Overall Project

    Team AssessmentA

    Chloride by flow(Cl not frommodels)

    Inconclusive (nowinter data) As the field data used to develop this figure do not include sampconclusions regarding chloride from this figure.

    Dissolved oxygenby flow

    Good Note the slight decline in the concentration of dissolved oxygencombination of decreased water agitation and higher temperaturwarm summer months).

    Fecal coliform byflow

    Moderate to Poor Generally, a pollutant that is present at high concentrations durin(fecal coliform, in this case) is attributed primarily to non-point years) would only contribute during the high flows when substa

    period with the highest flows, fecal coliform counts exceed the the standard is met more than 75% of the time. This would be thswimming, wading, etc.), although the amount of water in the st

    Phosphorus byflow

    Moderate to Poor Concentrations of phosphorus are greatest at high and low flowparticularly noticeable during low flows as well as non-point loasuspended sediment).

    Suspended solidsby flow

    Very Good toGood

    The concentrations of suspended solids increase with increased The suspended solids may come from runoff that carries a sedimstream sediments.

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    Flashiness Index

    Reach Description Richards Baker Flashiness Index

    RI-16 County Line Road 0.33

    Average Daily Flow

    County Line Road (823)

    0

    20

    4060

    80

    100

    120

    140160

    180

    200

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

    A V E R A G E D A I L Y F L O W

    ( C F

    S

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    Existing Water Quality Data

    AssessmentPoint

    Water QualityIndicator

    Statistic ConditioExis

    Mean (cells per 100 ml) 1,417Fecal 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)

    A v e r a g e

    N u m

    b e r o

    f D a y s

    P e r

    Y e a r

    Menomonee River @ County Line Road (RI 16)

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    Menomonee River @ County Line Road (RI 16)

    0

    40

    80

    120

    160

    200

    240

    280

    320

    360

    400

    0 -4 0 0

    4 0 0 - 6 0 0

    6 0 0 -1 0 0 0

    1 0 0 0 -2 0 0 0

    2 0 0 0 - 3 0 0 0

    Average Fecal Coliform (#/100ml)

    A v e r a g e

    N u m

    b e r o

    f D a y s

    P e r

    Y e a r

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    Menomonee River @ County Line Road (RI 16

    0

    40

    80

    120

    160

    200

    240

    280

    320

    360

    400

    0 - 0 . 0 5

    0 . 0 5 - 0 .1

    0 .1 - 0 .1 5

    0 .1 5 - 0 .2

    0 .2 - 0 .2 5

    0 .2 5 - 0 . 3

    0 . 3 - 0 . 3 5

    Average TP (mg/L)

    A v e r a

    g e

    N u m

    b e r o

    f D a y s

    P e r

    Y e

    a r

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    Menomonee River @ County Line Road (RI 16)

    0

    40

    80

    120

    160

    200

    240

    280

    320

    360

    400

    0 -2 5

    2 5 - 5 0

    5 0 -7 5

    7 5 -1 0 0

    1 0 0 -1 2 5

    1 2 5 -1 5 0

    Average TSS (mg/L)

    A v e r a g e N u m

    b e r o

    f D a y s

    P e r

    Y e a r

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    1

    10

    100

    1000

    0 10 20 30 40 50 6

    Flow Duration Interval (%

    C o n c e n

    t r a

    t i o n ( m g / L )

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

    County Line Road (RI-16) ReachChloride

    Modeled Flow Data; Chloride Field Data

    M id -ra nge F lo ws

    Hig h F lo ws

    Mo i st C on d i ti ons

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    1

    10

    100

    0 10 20 30 40 50 6

    Flow Duration Interval (%)

    C o n c e n

    t r a

    t i o n ( m g / L )

    Flow Conditions Regulatory Standard (5 mg/L)

    County Line Road (RI-16) ReachDissolved Oxygen

    Modeled Flow Data

    M id - ra nge F lo ws

    H ig h F lo ws

    M o ist C on d iti on s

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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 o n c e n

    t r a

    t i o n

    ( c f u / 1 0 0 m

    L )

    Flow Conditions Regulatory Standard (400 cfu/100 mL)

    County Line Road (RI-16) ReachFecal Coliform

    Modeled Flow Data

    M i d -ra n ge F lows

    Hig h F lows

    Mo ist C on diti ons

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    0.01

    0.10

    1.00

    0 10 20 30 40 50 6

    Flow Duration Interval (%

    C o n c e n

    t r a

    t i o n ( m g / L )

    Flow Conditions Planning Standard (0.1 mg/L)

    County Line Road (RI-16) ReachTotal Phosphorus

    Modeled Flow Data

    M id - ra nge F lo ws

    H i g h F lo ws

    M o ist C on d iti on s

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    1

    10

    100

    1000

    0 10 20 30 40 50 6

    Flow Duration Interval (%

    C o n c e n

    t r a

    t i o n ( m g / L )

    Flow Conditions Reference Concentration (17.2 mg/L)

    County Line Road (RI-16) ReachTotal Suspended Solids

    Modeled Flow Data

    M id - ra nge F lo ws

    H i g h F lo ws

    M o ist C on d iti on s

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