Utah Division of Water Rights

Proposed Management Plan for Salt Lake Valley Groundwater System

Revised: March 26, 1999
Contents
 
   
 
 
Figures
 

Figure 1 -- Salt Lake Valley Groundwater Management Plan Area
 

Figure 2 -- Method Used to Distribute Groundwater Withdrawals
 

1.0 Introduction
 

1.1 Background Information

The State Engineer implemented an Interim Groundwater Management Plan (Interim Plan) in Salt Lake Valley in April of 1991. The purpose of the Interim Plan was to address the over-appropriation of groundwater rights in Salt Lake Valley and to protect the quality of the resource while the United States Geological Survey (USGS) in cooperation with the public water suppliers and the Division of Water Rights conducted studies to determine the effects of large amounts of groundwater withdrawals on the water quality. These studies have been completed and are listed below:
 

A digital groundwater flow model for the Salt Lake Valley was developed in conjunction with the above technical publications. This model was created to simulate the various groundwater flow-related components -- recharge, rivers, canals and well withdrawals, for example -- of the aquifer system using physical properties of the aquifer such as hydraulic conductivity and storage coefficients. The impact of various withdrawal patterns on the long-term integrity of the aquifer can be reasonably determined by using the model. The model also provides a way to track the paths of water particles as they travel through the aquifer from areas of recharge to their points of discharge. It also has the ability to calculate well capture zones for various time periods.
 

The Interim Plan was intended to guide water management during the period of time the USGS studies were being conducted. In developing this long-term management plan for the valley, several provisions were added to the Interim Plan and some provisions were modified to reflect the information obtained from the studies. This groundwater management plan is intended to guide the long-term groundwater activities in Salt Lake Valley. This plan is presented as a proposal to the water users in the valley and to other interested parties and will be modified following their review and may also be modified as additional data becomes available. The boundary of the unconsolidated basin-fill material, which makes up the Salt Lake Valley aquifer system, is being used as the boundary of this management plan, as illustrated in Figure 1.

1.2 Modification of the Interim Groundwater Management Plan

The management areas used in the Interim Plan have been deleted and replaced with a different configuration designed to better deal with existing and potential problems in the aquifer system. The management areas of the Interim Plan were based, generally, on water quality data collected from 1979-1984 (DNR Technical Publication No. 89). The model has shown that those management areas would not be effective in preventing adverse effects on the aquifer caused by dense, localized withdrawals. In addition, the total amount of valley-wide groundwater withdrawals set forth in the Interim Plan have been modified based on information from the USGS studies.
 

1.3 Groundwater Management Plan Objective

The objective of this groundwater management plan is to allow for maximum utilization of the groundwater resource within the constraint of protecting the groundwater resources of Salt Lake Valley. The plan is proposed to help manage the groundwater resource so that water quality and existing water rights are protected. In proposing this groundwater management plan, the State Engineer is using his statutory authority to administer the measurement, appropriation, apportionment, and distribution of the groundwater of Salt Lake Valley.

 
 

2.0 Salt Lake Valley Groundwater Management Plan
 

The following policy guidelines are hereby proposed:
 

2.1 Groundwater Withdrawal Limits

In order to fulfill the objectives of this management plan, guidelines have been proposed to help distribute withdrawals on a regional and localized basis. If area or local withdrawals exceed the allowable respective withdrawal limits set forth in this plan, the State Engineer will distribute the water in accordance with the priority dates of the individual water rights using the following guidelines.
 

2.1.1 Regional Withdrawals from the Principal Aquifer

Everything in the Salt Lake Valley located to the east of the Jordan River shall be referred to as the "Eastern Region." The maximum average amount of withdrawal from the Eastern Region (based on a five year moving average) shall be 95,000 af/yr. The maximum withdrawal amount permitted in the Eastern Region in a single year shall be 120,000 acre-feet.
 

Everything in the Salt Lake Valley located to the west of the Jordan River shall be referred to as the "Western Region." The maximum average amount of withdrawal from the Western Region (based on a five year moving average) shall be 70,000 af/yr. The maximum withdrawal amount permitted in the Western Region in a single year shall be 90,000 acre-feet.
 

2.1.2 Sub-Regional Groundwater Withdrawals from the Principal Aquifer

In the Eastern Region there is a relatively large area of dense groundwater withdrawals. The majority of the groundwater withdrawals in the Eastern region are taken from that area. For management purposes, that area shall consist of Township 1 South, Township 2 South, and sections one through eighteen of Township 3 South, east of the Jordan River as shown on Figure 1. The maximum average amount of withdrawal from this area (based on a five year moving average) shall be 85,000 af/yr.
 

2.1.3 Localized Groundwater Withdrawals from the Eastern Region

A management grid has been set up based on the U.S. Public Land Survey's system. Under this system, the land is divided into section, township, and range. Each section is a square measuring approximately one mile on each side. In this management plan, one management square consists of any four sections, in a two section by two section configuration.
 

The maximum groundwater withdrawal rate from the principal aquifer in the Eastern Region for any square (a group of four sections) shall be 12,000 af/yr. Using this method, the squares overlap each other such that each section is actually part of four different management squares. Figure 2, below, illustrates how section 11 is part of four different management squares. Each of the four overlapping squares has a withdrawal limit of 12,000 af/yr.

FIGURE 2 - Method Used to Distribute Groundwater Withdrawals

2.1.4 Groundwater Withdrawals From the Shallow aquifer

Additional withdrawals above the allowable withdrawal limits set forth in this section will be allowed if such withdrawals are from the shallow aquifer, provided that such withdrawals do not have an adverse effect on other water rights.
 

2.1.5 Groundwater Withdrawals from Restricted Areas

There are two (2) restricted pumping areas currently in the plan, and are illustrated in Figure 1. These areas are associated with the following contaminated sites:
 

In order to protect the quality of the water by preventing changes in the vertical hydraulic gradient at these contaminated sites, the transfer of water rights into these areas will not be allowed. The restricted areas will be monitored to insure that current pumping in the area does not create a downward hydraulic gradient. These restricted areas are intended to be guidelines so that degradation of the principal aquifer system from contamination of the shallow aquifer does not occur. The restricted areas are based on available data and may change as new data is obtained. New restricted areas may be added to the plan upon evaluation of new data by the State Engineer and public review.
 

2.2 Applications to Change the Point of Diversion, Place of Use, or Purpose of Use

Change applications will be evaluated based upon their own merits. The evaluation may consider, but will not necessarily be limited to, potential impact on the following: existing water rights, the aquifer system as a whole, and overall water quality. The following guidelines will be used:
 

2.3 Proof of Appropriation/Change

In conjunction with all proofs of appropriation and proofs of change, the State Engineer shall require that the total volume of water to be certified has in fact been developed and placed to beneficial use. The State Engineer will review the total operation of a system or water user to ensure the intent of this requirement is met.
 

2.4 Well Spacing and Flow Rate

Well spacing and maximum flow rates of wells shall be regulated so a well, when pumped at its maximum flow rate, will not cause more than 12 feet of drawdown on any well with an earlier priority date. Users in a particular area may enter into an agreement to provide a variance from this requirement if it does not interfere with third party rights and also subject to approval by the State Engineer.

2.5 Applications to Appropriate Water and Segregation Applications

Applications to appropriate water from the principal aquifer will be considered for single family uses in non-subdivision areas where water is not available from a public water supply system. Applications to appropriate water will be limited to a maximum annual diversion of 1.0 acre-foot. The uses under such application shall not exceed the domestic purposes of one family, the irrigation of 0.10 acres, and/or the stock watering of a maximum of 10 head of livestock. Such rights shall be approved as fixed time applications for a ten-year period and upon the condition that when a public water system is available, the users will connect to the system, the well will be sealed, and the water right abandoned. Upon expiration of the ten-year period, if a public water supply system is still not available, such application will be extended upon proper filing of a request for extension.
 

All future segregation applications will be critically reviewed on their individual merits, according to current statutory provisions.
 

2.6 Extensions of Time for Applications to Appropriate Water

The State Engineer will critically review all future extension requests on approved applications to appropriate water pursuant to Section 73-3-12 of the Utah Code. In reviewing extension requests, if the State Engineer finds unjustified delays or a lack of due diligence, he may grant the request in part (including a reduction in the quantity of water available under the application), reduce the priority date, or deny the extension of time request.
 

2.7 Metering and Annual Reporting of Groundwater Withdrawals

All groundwater wells that have the right to potentially withdraw 50 acre-feet or more annually shall be equipped with a meter capable of measuring the instantaneous flow rate and total volume pumped through the meter. All water users meeting the above criteria shall be required to submit an annual report to the State Engineer by March 1 of each year setting forth the quantity of water diverted for each of their wells during the previous calendar year. Such reports shall summarize the monthly withdrawals for each well operated. If the water user submits an accurate and complete annual Utah Water Use Data Form it shall fulfill this requirement.
 

Owners of all groundwater wells that have the right to potentially withdraw 250 acre-feet or more annually, shall submit a water quality report for total inorganics every three years. A copy of the inorganic analyses performed as per Department of Environmental Quality, Division of Drinking Water requirements, will satisfy this reporting requirement.
 

2.8 Monitoring Activities and Aquifer Status Update

The Division will monitor the water quality reports submitted by the water users and give an updated, valley-wide water quality summary every 5 years. The Division will also provide water use information such as valley-wide, regional and localized withdrawals and priority lists.