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Water Budget III: Water Budget III:

Water Budget III: - PowerPoint Presentation

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Water Budget III: - PPT Presentation

Stream Flow P Q ET G Δ S Why Measure Streamflow Water supply planning How much water can we take out without harming ecosystems we want to protect Flood protection ID: 286482

water flow rainfall stage flow water stage rainfall discharge watersheds runoff velocity peak filtering time big relationship storage flows

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Presentation Transcript

Slide1

Water Budget III:

Stream Flow

P

=

Q

+

ET

+ G +

Δ

SSlide2

Why Measure Streamflow

?Water supply planningHow much water can we take out (without harming ecosystems we want to protect)Flood protectionHow much water will come down the channel if X storm happens? Who’ll be flooded?

Water quality

What are the fluxes

(flow x concentration)

of contaminants to a lake or estuary?

What are the effects of land use change on water delivery to downstream systems? Slide3

Stream Flow Network

(http://water.usgs.gov) Slide4

Extreme Low Flows

Rainfall between Oct 1. 2010 and January 21, 2011 is

2.68 inchesSlide5

Hydrograph- graph of flow over timeSlide6

Flow Over Time – Santa Fe RiverSlide7

Seasonality of FlowSlide8

Watersheds as Filters

Rain fallsStorages “buffer” the rainfall signal, letting water out slowlyMore storage = more bufferingThe result is that the rainfall signal looks stochastic, the flow looks more “organized”Watershed properties AND size affect the filtering effectSlide9

Rainfall Filtering – Santa Fe RiverSlide10

Rainfall Filtering – Finer ViewSlide11

Consider the “Filter” Effects of:

Watersheds with steep vs. shallow slopesWatersheds with deep vs. shallow soilsWatersheds with intense vs. extended rainfallWatersheds with forests vs. parking lotsWatersheds with dams vs. notBig vs. little watershedsWatersheds with big shallow aquifersSlide12

Basin Filtering Creates Lags – Hatchet CreekSlide13

Where is Stream Flow From?

At any time, flow is a composite of water with different sources and residence timesSome water is stored in the watershed for a very long time, some very shortDuring low flow conditions, water is mostly oldDuring storms, the contribution of new water increasesHow does an aquifer affect this?Slide14

2%

8%

23%Slide15

Flow and Rainfall Intensity

If Rainfall Intensity > Infiltration Capacity then surface runoff occursStream flows are composites ofSurface runoffSubsurface flowsSlide16

Variable Source Area

(Stormflow Generation in Florida)Slide17

Variable Source Area Makes Antecedent Rainfall IMPORTANTSlide18

Land Use (Cover) Affects Runoff Generation

Impervious surfaces preclude infiltrationLess infiltration means more runoffRunoff also MOVES faster Less “filtering”Compare land uses…Slide19
Slide20

More

stormflow, higher peak flow, sooner.Slide21

Forest

Ag

UrbanSlide22

Same total

flow (area under the curve),

lower peak flow.

The importance of

storage – the basis of filteringSlide23

Water Storage in the ForestSlide24
Slide25

D

epressions and vegetation (swamps) slow

runoff.

Upper watershed

wetland storage delays runoff and reduces peak flows.

Wetland flood plain

has

a dominant influence on downstream peak

flow and solute transport.

Wetland Hydrological ServicesSlide26

200,000 m

3

of

Stormwater

Runoff;

Channel Peak Flow capacity of 1m

3

/s

All in one day

Peak Flow =2.3 m

3

/s

Spread over 3 days

Peak Flow = 0.8m

3

/s

Why Does Storage Matter?Slide27

How Big a Flood Can We Expect?

The size of the flood is inversely proportional to it’s frequencyBig event happen rarelyBig events shape the landscapeMedium events maintain the landscapeSmall events control the biologyHow would we predict the size of a flood that happens roughly once in 25 years?Think back to the rainfall lab…Slide28

Rainfall Recurrence SeriesSlide29

Flow (Santa Fe River Station 3)Slide30

Daily Flow Recurrence SeriesSlide31

The 100-yr Floodzone

MapSlide32

How Do We Measure Streamflow?

Funny you should ask…basis of Lab #4.Basis is to estimate:Cross-sectional area (A; through which water flows)Water flow velocity (V)Q = A * VSlide33

Measuring Surface FlowSlide34

Typical stream velocity profileSlide35

Float Velocity * 0.8 for natural channels

Float Velocity * 0.9 for concrete channels

Where to measure mean velocity?Slide36

Turn-cup

0.500 ft/s

Electromagnetic

0.050 ft/s

Sonic Doppler

0.005 ft/s

$2k

$4k

$7k

Velocity InstrumentsSlide37

Sect

Width (m)

Depth (m)

Vel@.6 m/s

Flow

(m

3

/s)

1

1

0.7

0.20

0.14

2

1

2.0

0.25

0.50

3

1

1.3

0.15

0.20

Total

0.84m

3

/sSlide38

Discharge is HARD to Measure

We want:Daily (or sub-daily) measurementsMultiple stations per riverReal time updating (detect changes in flow as they are happening)Slide39

Rating equations (stage vs. discharge) allow continuous flow monitoringSlide40

Stage-Discharge Relation

Water stage (elevation) is EASY to measureStage is related to dischage via a mathematical relationship

Applying that relationship to measured stage gives estimates of discharge

Q

H

H

Q

t

t

Stage Hydrograph

Stage-Discharge Curve

or Rating Curve

Discharge HydrographSlide41

Stage-Discharge Relation

Typical relationship: Q = a(H +b)cThe relationship between H & Q has to be calibrated locally for different stationsSlide42

Stage Discharge Relationship for the Ichetucknee River

At low stage, positive relationship between stage and dischargeAt high stage, negative relationshipWhy?

Stage

DiscahrgeSlide43

Staff gage

Float-pulley

Pressure

Ultrasonic

Stage MeasurementsSlide44

WeirsSlide45

FlumesSlide46

Type

The Good

The Bad

Weir

Low cost

Easy installation

Won’t work on low gradient streams

Upstream flooding

Clogs

Changes WQ

Wildlife barrier

Flume

Works ok in low gradient streams

Better for WQ and wildlife Self cleaning

High cost

Difficult to install

Weir

vs

FlumeSlide47

What if there’s no rating curve?

New watershed, new conditionsAreas where it’s hard to develop rating curves

For example, the EvergladesSlide48

Q= 1/n * A * r

2/3 * s1/2

Q =

estimated flow m

3

/s

n = Manning’s

roughness

number

(0.02 smooth to 0.15 rough or weedy, 0.5 dense vegetation)

A =

cross sectional area (m

2

)

r

=

Hydraulic Radius (wetted

perimeter = WD/(W + 2D)

W > 10D, R → D)

s

=

Hydraulic Gradient

Δ

H/L

Manning’s Equation -

Flow Estimation without a rating equationSlide49
Slide50

Predicting Flow in the Everglades

Dense vegetation channel (n = 0.4)Shallow slope (s = 3 cm per km = 0.00003)Wide channel (100 m wide, 0.3 m deep, A = 30 m2, r = 30 m2 / 100.6 m = 0.3 m)

What is Q? What is flow velocity (u)?

Q = (1/n) * A * r

0.67

* s

0.5

V = Q / A

Q = (1/0.4) * 30 m

2

* 0.3 m

0.67

* 0.00003

0.5

= 0.183 m

3

/s

V = 0.183 m

3

/s / 30 m

2

= 0.006 m/s = 0.6 cm/sSlide51

Next Time…

Groundwater