HomeMy WebLinkAboutWGMeeting_PrelimPresentationWorking group meeting: Sustainable Management
Criteria for GW levels decline and Interconnected
Surface Water
April 9, 2021
Ukiah Valley Basin Groundwater Sustainability Agency
Draft
GOALS for today
1.Discuss strawman proposal for lowering groundwater levels and
depletion of interconnected surface water: possible option and
mutual impacts
2.We need to agree on the APPROACH, we can then refine the
numbers
⚫How can the model help in the decision?
⚫Evaluation of preliminary scenarios will inform some of our decision
2
Draft
SMC discussion: Groundwater Level Decline →OUR
STRAWMAN PROPOSAL
3
Draft
Hydrograph example
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600
605
610
615
620
625
630
635
640
391730N1232108W001
GW Elevation (ft)MT PT MO
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AquiferSite_Code Well_Name
Approximate
Distance to Russian
River (mi)
Buffer
(%)
Max Historical DTW
(ft)
X% of Max Historical DTW or 10'
(ft)
MT
(ft)
PT
(ft)
MO
(ft)
PT
(Spring Min)
(ft)
2 392962N1232047W001392962N1232047W001 0.30 10 57.8 5.8 63.6 57.8 17.5 13.6
2 392358N1232020W001392358N1232020W001 0.14 10 88.2 8.8 97.0 88.2 53.1 88.2
2 391730N1232108W00115N12W08L001M 0.98 20 30.1 6.0 36.1 30.1 26.4 25.3
2 391096N1231677W001391096N1231677W001 0.90 20 37.3 7.5 44.8 37.3 35.0 32.3
2 391285N1231607W001Ukiah Valley-34 1.60 20 22.7 4.5 27.2 22.7 21.5 12.1
2 391918N1232003W001Ukiah Valley-1 0.08 10 40.2 4.0 44.2 40.2 38.9 35.1
2 391918N1232003W002Ukiah Valley-2 0.08 10 49.9 5.0 54.9 49.9 47.7 45.6
2 391918N1232003W003Ukiah Valley-3 0.08 10 51.0 5.1 56.1 51.0 48.7 46.6
2 391918N1232003W004Ukiah Valley-4 0.08 10 52.0 5.2 57.1 52.0 49.6 47.9
2 391174N1231836W001Ukiah Valley-28 0.40 10 22.1 2.2 24.3 22.1 20.9 19.9
2 391411N1231983W002Ukiah Valley-37 0.85 20 57.9 10.0 67.9 57.9 50.1 57.9
2 391586N1232003W002Ukiah Valley-36 0.68 20 69.9 10.0 79.9 69.9 59.1 69.9
2 391860N1232039W001Ukiah Valley-15 0.18 10 24.0 2.4 26.4 24.0 22.8 20.8
2 392455N1231977W001Ukiah Valley-16 0.25 10 48.1 4.8 53.0 48.1 46.9 44.9
2 392455N1231977W002Ukiah Valley-17 0.25 10 93.4 9.3 102.8 93.4 92.1 93.4
2 392455N1231977W003Ukiah Valley-18 0.25 10 67.1 6.7 73.8 67.1 61.2 60.0
2 392572N1231906W001Ukiah Valley-9 0.75 20 40.3 8.1 48.3 40.3 37.2 22.5
2 T0604500280T0604500280 0.12 10 -----0.0
2 Ukiah WWTP-MW1Ukiah WWTP-MW1 0.22 10 -----0.0
2 South – Central #1(a)South – Central #1(a)0.35 10 -----0.0
2 North - Redwood Valley #1North - Redwood Valley #1 0.37 10 -----0.0
1 391918N1232003W001Ukiah Valley-1 0.08 10 40.2 4.0 44.2 40.2 38.9 44.2
1 391225N1231852W001Ukiah Valley-26 0.33 10 20.0 2.0 22.0 20.0 19.7 22.0
1 390664N1231491W001Ukiah Valley-32 0.24 10 24.8 2.5 27.3 24.8 23.8 27.3
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How do we reach the goal? PMAs!
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To be considered
◼How will these SMCs impact other Sustainability Indicators? And other beneficial users?
Will these SMCs for GW LEVELS be protective of them?
1.Well failure →quick calculation: if we go down 20 ft, about 10% of the wells in the basin may go dry
2.GDEs →with the approach that we are suggesting GDE will not be impacted more than the 2015
conditions
3.Sustainability Indicators: Interconnected Surface Water Depletion
→If yes: we move forward and agree on numbers for MT!!!
→If no: we need to reconsider the approach and reevaluate the numbers
◼How can we better understand the system?
⚫USE THE MODEL
⚫EVALUATE CLIMATE CHANGE AND MANAGEMENT SCENARIOS
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11/12/20
1. Forecasted well failure under a return to fall 2016 lows
well type n active n dry
domestic 276 6
agricultural 15 0
public 6 0
well type n active n dry
domestic 333 10
agricultural 19 0
public 10 0
31-year retirement age 40-year retirement age
~2%~3%
Land surface elevation
ft AMSL
11/12/20
Forecasted well failure under a return to fall 2016 lows minus 20 feet
well type n active n dry
domestic 251 25
agricultural 14 1
public 6 0
well type n active n dry
domestic 288 44
agricultural 18 1
public 10 0
31-year retirement age 40-year retirement age
~9%~12%
Land surface elevation
ft AMSL
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2. Impact to GDEs
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3. Impact to Interconnected Surface Water Depletion
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◼“Significant depletions of interconnected surface waters” means reductions in flow
or levels of surface water that is hydrologically connected to the basin such
that the reduced surface water flow or levels have a significant and
unreasonable adverse impact on beneficial uses of the surface water.
Draft
Interconnected Surface Waters
◼23 CCR §351(o)
“Interconnected surface
water” refers to surface
water that is hydraulically
connected at any point by
a continuous saturated
zone to the underlying
aquifer and the overlying
surface water is
not completely depleted.
Gaining
Losing disconnected
Losing connected
Draft
Depletion of Interconnected Surface Water
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◼Russian River is connected to the
groundwater system.
◼Establishing groundwater inputs vs. surface
water inputs is challenging.
◼Effects of groundwater capture from pumping
and surface water diversions on the river flow
increases complexity.
◼Lack of high-quality data to establish
thresholds.
◼Should we consider an adaptive approach for
SMCs?
Management Action
Trigger to avoid the
MT
VOLUME OF STREAM
DEPLETION THAT Leads
to Undesirable Result
Ideal
operating
range
Draft
Russian River reaches used as RMP’s
water balance calculations as monitoring type
◼We propose to calculate the impaired baseflow contributions for segments of
rivers in the Ukiah Watershed.
◼Impaired baseflow contribution is defined as the amount of groundwater
contribution between East Fork and Hopland considering releases, diversions,
and pumping.
⚫This is more a watershed objective: the GSA has control on PUMPING and with the
available data it is difficult to “discern” the contribution coming from pumping
◼Measurement locations will begin where there is data to establish thresholds
and be refined during the 5 -, 10-, and 15-year check-ins.
◼Utilizes monitoring locations already in place for better historical estimates.
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Draft
RMP logistics and assumptions
◼Russian River is highly dependent on inflow from Mendocino and
groundwater inputs late in the irrigation season.
◼Accurate August measurements will provide estimates of groundwater
contribution to the river.
◼Spatial aggregation means we can see changes in the system rather then
seeing changes in individual springs.
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𝐼𝑙𝑙𝑎𝑖𝑟𝑑𝑑𝑎𝑎𝑟𝑑𝑑𝑙𝑙𝑟=
𝐼𝑙𝑑𝑙𝑙𝑟−𝑂𝑟𝑟𝑑𝑙𝑙𝑟−𝑑𝑖𝑟𝑑𝑟𝑟𝑖𝑙𝑙𝑟
Draft
RMP Example calculation
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diversion
diversion
diversion
Inflow Outflow
Lots of Uncertainty in the diversions!
Draft
Assumptions to this approach
◼Estimates done in August and September to minimize impacts of surface
water flows, most of the tributaries become disconnected during the summer.
◼Estimates includes the groundwater capture from pumping, this is the
impaired baseflow.
◼Evaluation of project and managements actions better represented by the
model at the scale of this SMC.
◼Uncertainties in the diversion estimates
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Draft
Which METRIC can we use for ISW depletion?
◼Groundwater elevation as proxy
◼Streamflow measurements →we will have the transect data in 5 years!
◼Modified groundwater elevation proxy through gradient approach (EDF, 2018)
◼Volume of depletion calculated by the model: need better data to refine this
◼THIS IS THE APPROACH THAT WE SUGGEST:
ISW SMC= f(GWL) + f(impaired baseflow) + f(Measured/Modelled GW contribution to the
stream from transect data)
→ADAPTIVE SMC →transect data and therefore a new SMC will be available for the 5
years update
19
Draft
Which METRIC can we use for ISW depletion?
◼Groundwater elevation as proxy
◼Streamflow measurements →we will have the transect data in 5 years!
◼Modified groundwater elevation proxy through gradient approach (EDF, 2018)
◼Volume of depletion calculated by the model: need better data to refine this
◼THIS IS THE APPROACH THAT WE SUGGEST:
ISW SMC= f(GWL) + f(impaired baseflow ) + f(Measured/Modelled GW contribution
to the stream from transect data)
→ADAPTIVE SMC →transect data and therefore a new SMC will be available for the 5
years update
20
Draft
Questions concerning the approach?
Working group meeting: Sustainable Management
Criteria for GW levels decline and Interconnected
Surface Water
April 9, 2021
Ukiah Valley Basin Groundwater Sustainability Agency
Draft
Update on Integrated Model
Draft
Historical output from
Calibrated Model
3
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Historical output from
Calibrated Model
4
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Historical output from
Calibrated Model
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Historical output from
Calibrated Model
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Historical output from
Calibrated Model
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Draft
GSP Water Budget Requirements
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Historical
Evaluate how past water supply availability or reliability has previously affected aquifer
conditions and the ability of the local resource managers to operate the basin within
sustainable yield. Use at least the most recent ten years.
Current
Provide an accounting of current water budget conditions to inform local resource managers
and help the Department understand the existing supply, demand and change in storage
under the most recent population, land use, and hydrologic conditions.
Projected
Use 50 years of historical precipitation, evapotranspiration, and streamflow information as
the baseline condition to estimate future hydrology. Use the most recent land use,
evapotranspiration, crop coefficient, and water supply information.
Draft
GSP Water Budget Requirements
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1991-2018
2015-2018
20
1
8
-20
7
0
:
1
9
6
5
-20
1
8
Draft
GSP Water Budget Requirements
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Dataset/Condition Historical Current Future Baseline
(without PMAs)
Climate Change
(without PMAs)
Climate Condition Climate data from
1991-2018
Climate data from
2015-2018
Climate data from
1965-2018
Climate data from
2965-2018 multiplied
by DWR climate
change multipliers
Hydrologic condition
Known historical
hydrology from 1991-
2018
Known historical
hydrology from 2015-
2018
Known historical
hydrology 1965-2018
Modified hydrology
based on changes to
climate (ex. reservoir
releases)
Land Use 2010 Land Use 2010 Land Use 2010 Land Use 2010 Land Use
Ag Demand
Estimated demand
using IDC for 1991-
2018
Estimated demand
using IDC for 2015-
2018
Estimated demand
using IDC for 1965-
2018
Estimated demand
using IDC based on
climate data
Municipal Demand Available historical
data
Available historical
data 2018 demands 2018 demands
Draft
Hydrologic Periods
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Historical PeriodCalibration PeriodFuture Baseline
WY Type Historical Future
Above Normal 9 12
Below Normal 5 6
Critical 4 9
Dry 4 8
Wet 6 15
Period Length 28 50
Draft
Historical
Demands
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◼Groundwater pumpage falls between
6,000 to 7,000 AFY with small
changes in different water year
types.
◼In more recent years a 1000 AFY
swing can be seen from wet to dry
years.
Draft
Historical
Demands
13
◼SW Diversion falls mostly between
17,000 to 19,000 AFY with some
changes in different water year
types.
◼Municipal diversions have a
decreasing trend, assuming our data
is complete.
DraftHistorical Water
Budget –Basin
Boundary
14
Draft
Future Seepage
15
Draft
Climate Change
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◼DWR Climate Change Scenarios are run with the future baseline setting.
◼Reservoir outflows are assumed constant, and no change has been made to the demands.
Draft
Climate Change -Average Annual Budget Changes
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◼Water budget shrinks due to climate change impacts
◼All elements show declines (except pumpage that was assumed constant).
◼CC 2030◼Future Baseline ◼CC 2070
Draft
Climate Change -Impact on Groundwater Elevations
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◼A general decline can be expected, between 0-10 meters. Decline may be higher in the northern area than
the south. This is with the assumption that reservoir releases stay the same.
◼Maps show difference of CC-2070 and Future Baseline: Elevation=CC-2070elev-(Future baseline)elev
Draft
Summary
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◼Future Baseline
◼Basin storage is in balance and water budget dynamically resembles climatic conditions.
◼Budget is driven by the precipitation and recharge from basin area and outer watershed.
◼Basin may not provide similar seepage to the river in the future if conditions stay the same.
◼Climate change may decrease budget terms and limit the water available.
◼Climate change may decrease groundwater levels between 0-10 meters, higher declines expected
in the north and lower in the south. Model uncertainty is higher in the Redwood Valley area and
these results should be considered cautiously.
◼Assuming conditions stay the same, significant decline in storage is not observed.
◼Major data gaps exist, and impactful assumptions were made to run these scenario. Filling these
data gaps, including demand data, will improve model performance and accuracy of scenarios.
Draft
Exploratory/Informational Scenarios
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◼No Historical Supply
⚫We turned all diversion (Ag and Municipal) and pumpage (Ag and Municipal) off.
⚫Reservoir release is assumed constant and equal to historical releases.
⚫All other model input are held constant.
◼Business as usual:
⚫Equals our historical baseline
◼2x-Pumpage:
⚫We multiplied all pumpage (Ag and municipal) by 2.
⚫All SW diversions are equal to historical baseline.
⚫Reservoir release is assumed constant and equal to historical releases.
⚫All other model input are held constant.
Draft
GW Elevation Difference from Historical Baseline
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2x-Pumpage -Historical
Critical WY Type 2014
Fall (September)
2x-Pumpage -Historical
Above Normal WY Type 2017
Fall (September)
No Supply -Historical No Supply -Historical
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Future Seepage
22
Draft
Future Seepage
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Draft
Hopland Flow
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Draft
Questions?