IDAHO WATER RESOURCES RESEARCH INSTITUTE

Technical Assistance for Rural Ground Water Development in Idaho


Little Black Tail Ranch Development


Home

Reports and Publications

Project Site Data

Educational Programs

Fact Sheets

Related Links

Contact Us

Image Galleries I, II

Little Black Tail Ranch Development Publication

All Project Site Data

LITTLE BLACK TAIL RANCH DEVELOPMENT EXECUTIVE SUMMARY

INTRODUCTION

This report summarizes the results of the geologic/hydrogeologic services supporting the development of new water resources for the Little Black Tail Ranch Development (LBTR). The services are provided by the Idaho Water Resources Research Institute’s (IWRRI) Technical Assistance for Rural Ground Water Development Within Idaho program.

LBTR is located approximately 15 miles southeast of Sandpoint Idaho in the northern panhandle portion of Idaho. LBTR supplies about 70 people from two wells and a spring source. According to LBTR personnel the two wells do not produce significant quantities of water and the development relies predominantly on the spring collection system. It is our understanding that the spring collection system produces minimal quantities of water during late summer and greater production capabilities are needed to meet seasonal demands. LBTR has requested assistance in evaluating potential water well sites in the area to replace or supplement the spring collection and water well systems and provide greater water system capacity.

LBTR Water System

The LBTR water system supplies their service area with two water wells and a spring collection system. The spring collection system consists of three pump stations and associated collection devices. Currently only pump station #3 is utilized. Estimates of spring discharge as measured at the three pump stations range from 50 to 100 gallons per minute (gpm).

The two water wells (LBTR#6 and LBTR#15) were completed in May of 1999. Both wells have been reported to have flow rates at the time of drilling of between approximately 30 to 35 gpm. LBTR personnel report that the production rates of both wells have significantly decreased with use and can no longer supply the LBTR development with the necessary quantities of water.

GEOLOGIC SETTING

LBTR is located on the west shore of Lake Pend Oreille in the northern panhandle area of Idaho. The LBTR area is largely composed of three geologic units: 1) bedrock, 2) glacial deposits, and 3) recent unconsolidated sediments. The predominant rock type in the LBTR area is most likely derived by deposition of sediment in a narrow roughly north-south oriented ocean basin (in an area known as the Belt Basin). The predominant bedrock in the Hope area is the Belt Supergroup, composed of metamorphosed sedimentary rocks. Structural deformation of the Belt Supergroup over time has resulted in moderately dipping and highly faulted and fractured rocks that have been intruded by various types of igneous rocks.

Glaciation further modified this area apparently during at least two ice ages approximately 10,000 to 15,000 years ago. The glaciation deposited sediments consisting predominantly of silt, sand, and gravel. Recent unconsolidated sediments are derived from erosion of the upland area surrounding LBTR. The sediments are then transported downslope by gravity or within area streams.

HYDROGEOLOGIC SETTING

The LBTR area consists predominantly of metamorphic and intrusive igneous bedrock covered largely with glacial deposits. Review of available information for the LBTR area indicated the presence of two potential sources of ground water: 1) bedrock and 2) glacial/alluvial deposits. The weak stratigraphy and poor sorting within the glacial deposits most likely controls ground water flow. The igneous and metamorphic basement rocks within the LBTR area can be used as a limited water resource. Wells drilled into the basement rocks produce small quantities of water that are suitable for domestic purposes.

Bedrock is used as the primary ground water source for wells in the vicinity of LBTR. The aquifer is composed of fractures and/or faults in the bedrock. Wells completed in the bedrock typically obtain water from a number of fractures that will eventually contribute the desired quantity of water. Water well reports in the area indicate that wells completed upto 160 feet bgs result in yields ranging from 0 to 40 gallons per minute (gpm) averaging approximately nine gpm. There is some evidence that pumping at rates necessary for municipal supplies may result in a significant decrease in well yields over a short period of time.

The glacial/alluvial deposits in the LBTR vicinity represents a complex assemblage of sediments. The glacial/alluvial aquifers appear to be used as a secondary water well source and also produce springs that are used as a surface water source. There appears to be two aquifers, an upper and lower separated by the silt/clay unit. It appears based on the available water well reports that the silt/clay unit is continuous within the Krieger Creek Drainage.

The water elevation in the upper aquifer coincides very closely with the approximate water elevation of the springs observed near Pump Station #3. A reconnaissance of the spring collection system completed on April 20, 2003 showed significant quantities of water seeping from the south side of Krieger Creek near pump stations #2 and #3. At the time of the reconnaissance the combined overflow at pump stations #2 and #3 were estimated to be in excess of approximately 100 gpm. LBTR personnel indicated that the overflow ceases flowing during the summer months.

Aquifer Test and Analysis

A constant rate aquifer test was completed in Well #32 on April 22, 2003 using the existing submersible pump. The test was conducted to determine approximate aquifer properties. The well was pumped for about three minutes with discharge measured at a "frost free" spigot located at the wellhead. A maximum of 10.10 feet of drawdown was measured in the well with an average pump rate of 16 gpm. The subsequent transmissivity was calculated using the Cooper-Jacob Method. Based on the results of the limited aquifer test the calculated transmissivity is approximately 69 ft2/day. The aquifer test of well #32 is very limited in duration and pump rate and the transmissivity value and any subsequent interpretation should be used cautiously.

CONCLUSION

The potential locations for water well siting that may acquire yields greater than 60 gpm in the LBTR area are very limited. Based on existing information, the bedrock aquifers in the LBTR area do not appear adequate for municipal supply and are not considered as a potential target aquifer. There are two potential drilling sites located near LBTR with significant limitations for use as a municipal water well source. We would recommend the following that: 1) LBTR should continue to use the spring as their primary water supply, 2) the development of a 60 gpm well with the potential for long-term productivity in close proximity to the LBTR service area is unlikely. There is a possibility of developing a well near well #32 that may be used to supplement the spring collection system, 3) LBTR may also want to investigate the cost and benefit of further developing the current spring collection system as the primary municipal supply as opposed to completing a water well.