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The Great Salt Lake Water Budget - Great Salt Lake Advisory Council

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<strong>The</strong> <strong>Great</strong> <strong>Salt</strong> <strong>Lake</strong> <strong>Water</strong> <strong>Budget</strong><br />

David Tarboton<br />

Utah State University<br />

dtarb@usu.edu<br />

435‐797‐3172


Outline<br />

• General overview<br />

• Historic lake levels<br />

• Streamflow<br />

• <strong>Water</strong> <strong>Budget</strong><br />

• Future Simulations<br />

• Details if you want on<br />

– Bathymetry, Streamflow, Precipitation, Climate,<br />

Salinity, Evaporation


How a closed basin (e.g. GSL works)<br />

Inflows I<br />

I<br />

Evaporation depth E<br />

Evaporation volume E x A<br />

E x A<br />

Area, A<br />

E x A<br />

Area, A<br />

Volume, V<br />

<strong>Salt</strong> Load L<br />

<strong>Salt</strong> Concentration C=L/V<br />

Level<br />

Level<br />

If I > E x A level rises<br />

If I < E x A level falls<br />

Level adjusts to<br />

fluctuating inputs so that<br />

on average<br />

I = E x A<br />

I includes inflows from<br />

streams and precipitation<br />

on the lake<br />

I = Q + P x A<br />

Subject to climate<br />

variability.<br />

E is less variable, but also<br />

depends on climate and<br />

salinity, C.


GSL Level Record<br />

Level (ft)<br />

4195 4200 4205 4210<br />

16% 4195.6<br />

50% 4200.5<br />

South Arm USGS 10010000 <strong>Great</strong> <strong>Salt</strong> <strong>Lake</strong> at <strong>Salt</strong>air boat harbour, UT<br />

North Arm USGS 10010100 <strong>Great</strong> <strong>Salt</strong> <strong>Lake</strong> near Saline, UT<br />

South Arm water year mean<br />

84% 4205.6<br />

84% 4202.5<br />

50% 4198.9<br />

16% 4194.8<br />

Minimum level on Record 4191.4<br />

10/14/2010<br />

S 4193.7<br />

N 4193.2<br />

1900 1950 2000<br />

10/1/1949‐9/30/2010 period with complete<br />

climate and streamflow input data


Streamflow Inflows<br />

•Bear (10126000)<br />

•Weber (10141000)<br />

•Jordan<br />

− 10172550<br />

− 10170800 (Surplus<br />

Canal)<br />

− 10172630 (Goggin)<br />

•Davis<br />

− 10143500<br />

(Centerville)<br />

− 10141500 (Holmes)<br />

− 10142000<br />

(Farmington)<br />

− 10142500 (Ricks)<br />

− 10143000 (Parish)<br />

− 10144000 (Stone)<br />

− 10145000 (Mill)<br />

•Other<br />

− 10141040 (Hooper)<br />

− 10141400 (Howard)<br />

− 10172640 (Lee)<br />

− 10172650<br />

(Kennecott)


<strong>Water</strong> <strong>Budget</strong><br />

V<br />

<br />

Q<br />

<br />

P<br />

A<br />

<br />

E<br />

A<br />

• Q, Streamflow+Groundwater‐Withdrawals<br />

– Groundwater 75000 acre ft/yr (Waddell and Barton,<br />

1980)<br />

– Withdrawals (West desert pumping, Evaporation<br />

ponds)<br />

• A, V Area and Volume<br />

– From bathymetry and level<br />

• P, Precipitation<br />

– From PRISM (Oregon State University)


<strong>Water</strong> <strong>Budget</strong> Summary<br />

(thousand Acre ft/yr)<br />

1949/10‐2008/9 2003/10‐2008/9<br />

Bear 1347 986<br />

Jordan 495 425<br />

Weber 338 242<br />

Davis 31 30<br />

Other 105 95<br />

All Streamflow 2316 1778<br />

Direct Precipitation 876 781<br />

Groundwater 75 75<br />

Evaporation (‐3666 3 ) ‐3264 2 (2961 3 ) ‐2834 2<br />

Adjustments ‐39 1 0<br />

Ave Vol Change ‐32 ‐212<br />

Notes:<br />

Closure ‐4 12<br />

1. Net west desert pumping loss averaged over 59 years<br />

2. Mass balance evaporation<br />

3. Calculated evaporation


Future simulations<br />

• <strong>Water</strong> budget model with inputs P, Q<br />

• Inputs resampled from historic years<br />

retaining each year as a block<br />

• Resampling used k‐nearest neighbors<br />

(based on total streamflow) to sample<br />

similar years together and maintain<br />

statistical dependence<br />

• Evaporation used either the historic<br />

value from mass balance, or was<br />

calculated from salinity as a function of<br />

volume (C=L/V)<br />

• Level differences between arms not<br />

modeled<br />

• Pumping limits level to 4208 ft<br />

-0.2 0.0 0.2 0.4 0.6 0.8 1.0<br />

Annual streamflow autocorrelation from knn<br />

0 2 4 6 8 10 12 14 16<br />

Lag years


100 resampled input simulations<br />

10 year simulations<br />

Distribution of 10 year ahead<br />

Levels<br />

4185 4190 4195 4200 4205<br />

Frequency<br />

0 5 10 15 20<br />

2010 2012 2014 2016 2018 2020<br />

4190 4195 4200 4205<br />

Level (ft)


Simulated <strong>Water</strong> <strong>Budget</strong> Sensitivity over<br />

2003/10‐<br />

2008/9<br />

next 10 years<br />

(thousand Acre ft/yr)<br />

16%<br />

(‐1 std dev)<br />

50%<br />

(median)<br />

84%<br />

(+1 std dev)<br />

All Streamflow 1778 1801 2067 2857<br />

Direct<br />

Precipitation<br />

781 818 891 1252<br />

Groundwater 75 75 75 75<br />

Evaporation (ft) 3.58 3.48 3.31 3.47<br />

End Level 4194.1 4191.6 4195.6 4199.5<br />

Conclusions<br />

•8 ft range possible over next 10 years ahead due to natural variability<br />

•Human or natural reduction in streamflow of 260 000 acre ft/yr below<br />

median could drive level down to near 4191 ft in next 10 yr<br />

•Without change lake most likely to stay near current levels<br />

•About 13% chance lake may even rise above 4200 ft in next 10 years


Bathymetry<br />

South Arm<br />

North Arm<br />

Level (ft)<br />

4170 4180 4190 4200 4210<br />

Baskin 2005<br />

Loving 2000<br />

Baskin 2005 + Farmington Bay<br />

+MagCorp ponds<br />

Level (ft)<br />

4170 4180 4190 4200 4210<br />

Baskin 2006<br />

Loving 2000<br />

0 200000 600000 1000000<br />

0e+00 2e+05 4e+05 6e+05 8e+05 1e+06<br />

Area (acre)<br />

Area (acre)<br />

the lake bed topography that relates area<br />

to level and volume


Using “steady state” to evaluate potential<br />

impact of pond withdrawals and<br />

bathymetry on lake level<br />

• Inputs<br />

– Evaporation, E (from climate)<br />

– Area, A (from low, median,<br />

high percentile levels)<br />

• Net inflows estimated from<br />

“steady state”<br />

– I=A x E<br />

• Withdrawal subtracted<br />

from net inflow and<br />

modified area determined<br />

– A'= (I‐W)/E<br />

1,055,576<br />

979,500<br />

Area (acre)<br />

• Level determined from<br />

bathymetry (modified)<br />

4194 4196 4198 4200 4202 4204 4206<br />

4199.9<br />

600000 800000 1000000 1200000 1400000<br />

Current<br />

Modified<br />

1,055,576<br />

979,500<br />

4199.9<br />

4200.6<br />

level (ft)<br />

the sensitivity is greater when the arealevel<br />

function is flatter


GSL streamflow inputs<br />

Ac ft<br />

2e+05 4e+05 6e+05 8e+05 1e+06<br />

Total<br />

Bear<br />

Weber<br />

Jordan<br />

Davis<br />

Other<br />

Monthly streamflow from USGS<br />

gauges with regression to fill<br />

missing values<br />

1950 1960 1970 1980 1990 2000 2010<br />

Annual average GSL Streamflow inputs (Acre ft)<br />

Bear Weber Jordan Davis Other Total<br />

1347346 338385 494874 30783 104832 2316220<br />

58% 15% 21% 1% 5% 100%<br />

Loving, et al., (2000), USGS 00‐4221. Calculated inflows for the period 1987‐1998. <strong>The</strong>se<br />

methods with minor adjustments were applied to obtain streamflow from 1949 to 2008


Precipitation<br />

inches/month<br />

0 1 2 3 4 5<br />

South<br />

North<br />

Monthly<br />

1950 1960 1970 1980 1990 2000 2010<br />

inches<br />

0 5 10 15 20<br />

South<br />

North<br />

Annual<br />

1950 1960 1970 1980 1990 2000 2010<br />

Monthly PRISM climate data for the U.S. from Oregon State University from<br />

http://www.prism.oregonstate.edu/


Other climate variables<br />

Degrees C<br />

-10 0 10 20 30 40<br />

South Max North Max South Min North Min<br />

1950 1960 1970 1980 1990 2000 2010<br />

• Monthly averages of daily maximum and minimum<br />

temperatures from PRISM (shown)<br />

• Monthly average of daily dewpoint from PRISM (not shown)<br />

• Monthly average of daily wind speed from University of<br />

Washington (not shown)


<strong>Great</strong> <strong>Salt</strong> <strong>Lake</strong> Inputs<br />

acre ft<br />

0e+00 4e+06 8e+06<br />

Total<br />

Streamflow<br />

Precip<br />

Groundwater<br />

W Desert Pumping<br />

W Desert return<br />

1950 1960 1970 1980 1990 2000 2010<br />

Adjustments to GSL inputs<br />

•West Desert pumping. 2.5 MAF removed 4/87 to 6/89. 27<br />

months<br />

• 200000 AF return from West Desert. 1/90 to 6/92. 30 months<br />

Wyr


Total <strong>Salt</strong> Load<br />

Billion tons<br />

0 1 2 3 4<br />

LVG4 [north]<br />

RD2 [north]<br />

FB2 [south]<br />

AS2 [south]<br />

3.89 billion tons<br />

Total<br />

North<br />

South<br />

4/87‐6/89<br />

West desert<br />

pumping<br />

1/90‐6/92<br />

West desert<br />

return flow<br />

3.64 billion tons<br />

1970 1980 1990 2000<br />

Calculated from volume and depth average<br />

measurements. Data from Wally Gwynn (UGS)


<strong>Salt</strong> concentrations<br />

C g/L<br />

0 50 100 200 300<br />

LVG4 [north]<br />

RD2 [north]<br />

FB2 [south]<br />

AS2 [south]<br />

Causeway closure<br />

1950 1960 1970 1980 1990 2000 2010<br />

Salinity computed from C=L/V for each arm<br />

(lines) and compared to observations


Salinity dependent evaporation<br />

Penman evaporation equation modified for salinity<br />

(Mohammed, 2008)<br />

E<br />

'<br />

R<br />

<br />

n<br />

'<br />

<br />

Where:-<br />

R n Net Radiation,<br />

λ v latent heat of vaporization,<br />

β water activity coefficient,<br />

ν a wind speed ,<br />

e<br />

( T,<br />

S)<br />

<br />

∆' gradient of saturated vapor content of air corrected<br />

for salinity,<br />

γ psychrometric constant,<br />

s<br />

<br />

e<br />

T<br />

K E bulk transfer coefficient.<br />

v<br />

w<br />

s<br />

<br />

s<br />

<br />

'<br />

e<br />

s<br />

e<br />

( T ) ( T,<br />

S)<br />

s<br />

K<br />

<br />

T<br />

s<br />

E<br />

<br />

a<br />

( e<br />

s<br />

( T<br />

a<br />

) (<br />

T<br />

Ebrine/Efresh<br />

a<br />

0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0<br />

, S)<br />

e<br />

a<br />

)<br />

0 100 200 300 400<br />

TDS (g/L)


Annual GSL Evaporation<br />

meters<br />

0.4 0.6 0.8 1.0 1.2 1.4<br />

Mass balance<br />

N brine<br />

N fresh<br />

S brine<br />

S fresh<br />

10 20 30 40 50 60<br />

inches<br />

1950 1960 1970 1980 1990 2000 2010<br />

Mass Balance<br />

E<br />

<br />

P<br />

N<br />

A<br />

N<br />

<br />

PS<br />

A<br />

A<br />

S<br />

N<br />

Q <br />

A<br />

S<br />

W<br />

V


Predictive Mass Balance Model<br />

• Inputs<br />

– Precipitation (N and S)<br />

– Evaporation (Historic or Calculated)<br />

– Streamflow<br />

– Initial Level<br />

• Output<br />

V<br />

Q P A<br />

– Levels and volumes<br />

<br />

E A


Verification with historic inputs<br />

Level<br />

4190 4195 4200 4205 4210<br />

North Obs<br />

South Obs<br />

Mass Bal. E<br />

Climate E<br />

1960 1970 1980 1990 2000 2010

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