HomeMy WebLinkAboutResolution 2014-001 agreement to continue water resources studyMARANA RESOLUTION NO. 2014-001
RELATING TO UTILITIES; APPROVING AND AUTHORIZING THE UTILITIES DIRECTOR
TO EXECUTE A JOINT FUNDING AGREEMENT WITH THE U.S. DEPARTMENT OF THE
INTERIOR U.S. GEOLOGICAL SURVEY TO CONTINUE FROM OCTOBER 1, 2013
THROUGH SEPTEMBER 30, 2016 THE STUDY ENTITLED AQUIFER-STORAGE CHANGE
AND LAND-SURFACE ELEVATION CHANGE MONITORING IN THE TUCSON ACTIVE
MANAGEMENT AREA
WHEREAS the U.S. Geological Service, the Town of Marana, the City of Tucson, Pima
County, the Town of Oro Valley, Metropolitan Domestic Water Improvement District, and the
Arizona Department of Water Resources have since 2003 been j ointly funding a study of changes in
aquifer storage and land-surface elevation in the Tucson Active Management Area; and
WHEREAS the land subsidence and aquifer storage proj ect provides information needed for
the development of water resources and land planning.
NOW, THEREFORE, BE IT RESOLVED BY THE MAYOR AND COUNCIL OF THE
TOWN OF MARANA, ARIZONA, as follows:
SECTION 1. The Joint Funding Agreement between the Town of Marana and the U.S.
Department of the Interior U.S. Geological Survey attached as E�iibit A to and incorporated in this
resolution by this reference is hereby approved, and the Utilities Director is hereby authorized to
execute it on the Town's behalf.
SECTION 2. The various Town officers and employees are autharized and directed to
perform all acts necessary or desirable to give effect to this resolution.
PASSED AND ADOPTED BY THE MAYOR AND COUNCIL OF THE TOWN OF
MARANA, ARIZONA, this 7 day of January, 2014.
ATTEST:
`-� �' �.�
�
Mayor Ed Honea
APPROVED AS TO FORM:
/ / /
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Resolution No. 20�4-001 12/18/2013 1:49 PM
Form 9-1�66
(oct. zoas)
U.S, t3EFA�2TM�iVT �� T'NE fi��'E�il�l�i
GEI�L,t�GICAL St1RifEY
10tMT �UN[�ING AGREEMENT
[�il:i
WATER RESOURCES INVESTIGATIONS
Amount Date to
$16,950.00 October 1, 2013
6000000832/AZ066
14 WSAZ00400
ZF009EF
86-6000266
YES
THIS AGREEMENT is entered into as of the,l0th day of December, 2013 by the U.S. GEOLOGICAL SURVEY, UNITED
STATES DEPARTMfNT OF THE INTERIOR, party of the first part, and the TOWN OF MARAPIA, party of the second
part.
�' The parties hereto agree that subject to availability of appropriations and in accordance with their respective
authorities there shall be maintained in cooperation an investigation of aquifer storage change and land
subsidence in the Tucson easin and Avra Valley as described in the attached workplan, herein called the program.
The USGS legal authority is 43 USC 36C; 43 USC 50; and 43 USC 50b.
2. The following amounts shall be cantributed ta caver a11 of the cost of the necessary field and analytical work
directly refated tn this program. 2(b) inciudes in-Kind Services in the amount of $0.00
(a} by the party af the first part during the period
(b) by the party of the second part during the period
Amount Date
(c)
�dy
$22,500.00 October 1, 2013
Customer #:
Agreement #:
Project #:
TIN #:
Fixed Cost
Agreement
Date
September 30, 2016
to
Date
September 30, 2016
Total = $39,450.00
AdditionaE or reduced amaunts by each party during the above period or succeeding periods as may be
determined by mutual agreement and set forth in an exchange of letters between the parties.
The perfiormance period may be changed by mutual agreement and set forth in an exchange of letters
between the parties.
3. The costs of this program may be paid by either party in conforrnity with the laws and regulations respectively
governing each party.
4. The field and analytical wnrk pertaining to this program shall be under the direction of or subject to periodic review
by an authorized representative of the party of the first part.
S. The areas to be included in the pragram shall be determined by mutual agreement between the parties hereto or
their authorized representatives. The methods employed in the fie(d and office shali be those adopted by the party
of the first part to insure the required standards af accuracy subject modificatian by mutuai agreement.
6. During the cnurse nf this program, all field and analytical work of either party pertaining to this prpgram shall be
open to the inspection nf the other party, and if the work is not being carried on in a mutually satisfactory manner,
either party may terminate this agreement upon 60 days written notice to the other party.
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7. The cari��rt�l re�atds resc�it��t� fr�m this �ra�r��n iu�l[ b� d�pr��ited in t�� aific� c�f €�ri�tr� �f ttrcise r�cca€ds. Upc�n reque�t;
r;c�p'res of the c�r€�in�p r�c�r�ls wE(I �� �rrc�vided tc� �he c�ffice �f t�te c�th�r part�!.
E�. Ttre rr��ps; r�cords, or €�parCs rssuiti�t� frcrrr� tt�is pca�r�rrr s�a�it be ��cfe aua�tabEe tc� th� �ub�ac as �r�mptly �� per�sibie: Ttt�
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Aquifer-Storage Change and Land-Surface Elevation Change
Monitoring in the Tucson Active Management Area
FY 2014-2016
Introduction
Aquifer-storage change has been monitored by the U.S. Geological Survey (USGS)
within the Tucson Active Management Area (AMA) since 1996. The USGS began a
cooperative study with Metropolitan Domestic Water Improvement District and the town
of Oro Valley in 1996 to monitor aquifer-storage change in the Lower Canada del Oro
subbasin. In 1998, the USGS began a cooperative study with the Arizona Department of
Water Resources (ADWR), Pima County, and the City of Tucson to monitor land-surface
elevation change and aquifer-storage change in the Tucson AMA. In 2003, these two
monitoring studies were combined, and the town of Marana joined the study. This
proposal outlines a scope of work for continued and expanded monitoring of both
aquifer-storage change and land-surface elevation change in the Tucson AMA for the
period of October 1, 2013 through September 30, 2016.
Aquifer-Storage Change
Aquifer-storage change can be monitored by measuring changes in graviTy. As water is
added or removed from the aquifer, there is a change in mass and a corresponding
measurable change in gravity. Gravity also is affected by changes in land-surface
elevation, so mnnitoring of land-surface elevation change is essential for accurate
measurement of aquifer-storage change.
Water levels in wells commonly are monitored to estimate aquifer-storage changes.
However, use of water-level variations entails significant assumptions about the
hydraulic properties of the aquifer system. One difficulty is the heterogeneity of
hydrologic properties of the aquifer; the alluvial sediments of the aquifer vary in
lithology and texture, both laterally and with depth. Thus, data from individual wells may
not represent aquifer characteristics some distance away from the well. A second
difficulty is monitor-well design; in Tucson Basin, most water levels are measured in
deep wells that tap multiple aquifer layers, most of which are confined and have
accordingly low storage properties. Water levels in these deep wells are a composite of
water ievels from several aquifer units. When these composite water levels are used to
estimate storage changes, the hydrologic properties used in the calculation typically do
not reflect the range of aquifer materials over which the well is screened. Because of
these complexities and requisite assumptions, use of water-level variations as the only
indicators of stora�e change can be uncertain, and cannot be reliably extrapolated beyond
the well location.
Monitoring of gravity and water levels in Tucson Basin has shown that large changes in
groundwater storage, as much as several feet of water, have occurred that were not
reflected in comparable water-level changes. Water levels following intense precipitation
and infiltration, and associated gravity increases, either tend to rise slightly or to cease or
slow their declines as gravity declines. These responses generally are manifested up to a
year after the storage increase. The extent to which water levels are influenced by
storage changes are directly related to the proximity of the well to the recharge area.
Closer proximity yields an earlier and more discernible water-level response. Water-
level responses also depend on the geometry and lithology of the sedimentary layers in
the aquifer system that wells sample. Typically this information is missing, incomplete,
or uncertain. Ail of this points to the need for a combination of storage-change and
water-level data, which together enable defensible estimates of aquifer specific yield
distribution.
Land-Surface Elevation Change
Permanent land subsidence can occur in alluvial basins when water is removed from
aquifer systems (Galloway and others, 1999). Aquifer systems in unconsolidated rocks
such as those in the Tucson AMA are supported by the granular skeleton and the pore-
fluid pressure. When groundwater is withdrawn and the pore-fluid pressure is reduced,
the granular skeleton is compressed, causing some lowering of the land surface. Both the
aquifers (sand and gravel) and aquitards (clay and silt) of aquifer systems are deformed as
a result of changes to the pore-fluid pressure and skeleton, but to different degrees. Most
permanent subsidence occurs due to the irreversible compression of aquitards during the
slow process of aquitard drainage (over a number of years).
Permanent subsidence, seasonal elastic deformation, and uplift have been observed in
Tucson Basin and Avra Valley. Rates of compaction in Tucson Basin in relation to water-
level decline have been less than 0.5 foot per 100 feet of water-level decline. Comparison
with the Eloy and Phoenix areas (greater than 1 foot per 100 feet of decline) suggests that
compaction to date in the Tucson region has been largely elastic and recoverable.
Compaction and land subsidence can be slowed or stopped, and in areas having
appropriate geologic conditions, reversed to some extent by eliminating groundwater
withdrawals or through artificial recharge.
The City of Tucson has increased delivery of Central Arizona Project (CAP) water, while
reducing pumping from the Central Well Field. This has reduced water-level declines;
however, subsidence due to previous pumpage may continue for some time into the
future. Continued monitoring of areas having the greatest potential for subsidence will
provide information that municipalities and resource managers can use in the
development and implementation of prevention and mitigation efforts.
Objectives
The objectives of this project are to monitor aquifer-storage change and land-surface
elevation change within the Tucson AMA.
2
Approach
Land-surface elevation change is monitored at a network of benchmarks (figure 1)
throughout the Tucson AMA by measuring changes in land surface elevation over time
(approximately annually) with Interferometric Synthetic Aperture Radar (InSAR) and
targeted GPS surveys. The Arizona Department of Water Resources (ADWR) has an
InSAR program in the Tucson AMA. InSAR is a technique that utilizes interferometric
processing to compare the amplitude and phase signals received during one pass of the
satellite-based SAR platform over the AMA with the amplitude and phase signals
received during a second pass of the platform over the same area but at a different time.
The SAR data are used by ADWR to produce a land-surface elevation-change map over
the same time period as the targeted GPS surveys in the AMA. The GPS data is then used
to compare with and constrain the InSAR deformation information. The annual InSAR
product provides a much broader coverage of land-surface deformation information than
could be feasibly obtained with GPS alone.
Aquifer-storage change is monitored by measuring changes in gravity over time at the
same network of benchmarks. Gravity is affected by mass and distance; a change in mass
or a change in elevation will cause a change in gravity. Groundwater depletion is a mass
change and land-surface elevation change is a distance change. By removing the effect of
change in distance, changes in gravity are used to determine changes in aquifer-storage.
Temporal-gravity surveys are used in the Tucson AMA to detect local changes in the
gravitational field of the Earth. The method is readily applied to measurement of aquifer-
storage change in the AMA because of the occurrence of significant variations in pore-
space storage that result from groumdwater withdrawal and periodic (non-continuous)
focused recharge. Two instruments are used at the network of benchmarks: the relative
gravity meter and the absolute gravity meter. The relative meter is the primary instrument
by which differences in gravity are monitored at stable monuments. Much as control
benchmarks are used in conventional land surveying, repeated relative gravity surveys for
groundwater storage monitoring should include a reference station where gravity is
known to vary little, or the absolute acceleration of gravity is monitored. The USGS uses
a Micro-g LaCoste A-10 field-portable absolute gravity meter to establish these reference
stations as needed. This is particularly valuable in a hydrologic context where a number
of absolute stations may be located throughout a basin, thereby serving to constrain a
least-squares adjustment of the network of gravity differences from relative gravity
surveys.
Gravity surveys are conducted annually at the entire network of benchmarks (figure 1).
GPS surveys also are conducted annually at the portion of the network that previous
surveys have shown to be the most active areas of land-surface elevation change. The
network of benchmarks may be modified and/or expanded in areas of poor coverage to
improve resolution. These areas include Avra Valley, Sahuarita, and central Tucson.
Gravity measurements will increasingly be made using the A10 portable absalute
gravimeter; this will allow for fewer relative gravity measurements, thus improving the
efficiency of data collection.
Fig. 1. Proposed network for aquifer-storage and subsidence monitoring in the Tucson
AMA.
Bene�ts
Aquifer-storage monitoring
Microgravity surveys are an efficient, noninvasive means of ineasuring changes in the
amount of groundwater in Southwestern alluvial basins. Monitoring changes in
groundwater storage in the Tucson AMA is a means to monitor the status of the basin
aquifers. This will be of value as water-supply entities in eastern Pima County address
needs to manage and augment groundwater resources. The most significant value would
accrue as the city further implements aquifer storage and recovery efforts at the
Clearwater Renewable Resource Facility (CRRF). As the CRRF reaches anticipated
capacity, pumping from the Central Well Field will continue to be reduced. This
decreased demand will, if withdrawals do not increase, enable the aquifer to slowly refill.
Water-level data entail assumptions about aquifer and well properties; thus, monitoring of
gravity changes as pumping decreases in the basin currently is the only way to measure
attendant changes in the amount of water in the aquifer and determine if and when
aquifer recovery is occurring. This information conceivably will serve as part of a basis
for decisions regarding distribution of groundwater withdrawals to help in mitigating land
subsidence or aquifer storage losses in particular areas.
Aquifer-storage change is one of the three components of the groundwater budget. The
other two are inflow to and outflow from the aquifer system. Measurement of aquifer-
storage change and measures and estimates of outflow enable better estimation of
recharge and development of a more reliable groundwater budget for the basin. Measures
of aquifer-storage change increase the reliability and utility of groundwater flow and
management models. Use of storage-change data to improve model calibration enables
addttional reduction in the uncertainty of model results. The improved understanding of
the movement, distribution, volume, and availability of ground water, to which storage
monitoring contributes, enables more effective water management in the Tucson AMA
and in other areas of the State.
Surveys in the Tucson AMA since 1998 have provided previously unavailable data
quantifying recharge and storage changes. For example, the results of aquifer-storage
change monitoring in the Tucson Basin between 1998 and 2012 indicate that storage
change and recharge can vary considerably from year to year. It is possible that just a
few years may account for the majority of recharge to southwestern aquifers for an entire
decade or more. These data are being used to improve the understanding of the aquifer
systems and to improve groundwater flow models that will be used in resource planning.
4
Land-surface elevation change monitoring
Some types of infrastructure are more sensitive to changes in land slope than other types.
Sewer systems are largely gravity driven, and aze designed and constructed at slopes of
about 2 feet per 1,000 feet. Small slope changes can cause operational problems under
some conditions. Accurate determination of the rates, amounts, and distribution of land
subsidence, together with delineation of higher-risk areas, will provide data upon which
mitigation and protection plans can be based.
Subsidence rates will increase when the stress threshold between elastic and inelastic
compaction is exceeded. Because it is not possible to reliably estimate when the
threshold might be exceeded in the Tucson AMA, and infrastructure damage becomes
more likely, subsidence monitoring also provides a means to identify the type of
compaction that is occurring.
Groundwater withdrawals from the City's Central Well Field has been substantially
decreased as the CRRF reaches full capacity. However, regional subsidence in response
to previous pumping is unlikely to end in the near future. It will continue until the
aquifer system reaches pressure equilibrium. Observation of the timing and magnitude of
aquifer responses will further improve the understanding of land subsidence and of how
the aquifer systems function. Monitoring data also will contribute to a better
understanding of the responses of the aquifer systems to withdrawals, and will provide
additional insight in future plans for well-site selection, recharge efforts, and water-
management programs. Additionally, monitoring data will continue to augment and
serve as ground truth for satellite-based information that the ADWR is acquiring to
enable broad-scale assessments of regional subsidence in the Tucson Basin.
Differential subsidence refers to a relatively large amount of subsidence over a relatively
short distance, and can cause focused effects. For example, localized subsidence of as
little as one-half inch can necessitate rebuilding a highway overpass. Differential
subsidence has the potential to separate pipe joints of sewer and water lines—this can
lead to system disruptions and roadway damage. Also vulnerable are the concrete lining
sections of engineered channels that rely on the integrity of expansion joints to prevent
flood damage. Costs to address such infrastructure failures are high. Awareness of the
distribution and magnitude of differential subsidence can help to guide the design and
implementation of maintenance and monitoring schedules, selection of monitoring
methods, and the design and construction of future infrastructure.
Products
1) Annual interpretive maps of aquifer-storage change and land-surface elevation
change in the Tucson AMA (available to all cooperators and to the public on
http://az.water.usgs.gov�.
2) Oral presentation of findings to all cooperators each year.
3) Oral presentation of findings at a state or national professional society meeting
each year or as funding permits.
6
Work Schedule and Budget
Fixed-cost funding information for this project is provided in tables 1 and 2. Table 1
presents the schedule of work activities over the project life. Table 2 presents the
summary of funding by agency. It is understood that all agency funds in future years are
subject to appropriation.
Table 1—Schedule of work activities.
Work Tasks Year 1 Year 2 Year 3
1. GPS and InSAR surve s
2. Gravi surve s
3. Data post rocessing, analysis, and inter retation
.
z
4. Preparation of annual digital maps of aquifer-storage
change
and land-surface elevation change `
5. Oral Report to project cooperators
6. Oral Presentation at state or national rofessional meeting
,.
7. Review, revision and approval of annual maps of
a uifer-stora e chan e and land-surface elevation chan e
8. Posting of annual maps to http://az.water.usgs.gov/
and distribution to roject cooperators
7
Table 2—Summary of funding by agency.
Note: Funding distributions shown are proposed for the FY14-16 project period. A table
reflecting the final distribution will be provided to all participants following completion of
funding agreements.