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BUREAU OF LAND MANAGEMENT

BIN REPORT

TITLE:  Effects of Siltation and Salinization of the San Juan River on the Survival and Recovery of the Colorado Squawfish and Razorback Sucker   

SUBMITTING BUREAU:    Bureau of  Land Management

BIN NUMBER:                                 BLM04CR98

BRD REGION:                                 Central

DESCRIPTION OF NEED: The San Juan River originates high in the San Juan Mountains of southwestern Colorado and flows in a southwesterly to westerly direction where it ends at the confluence with the Colorado River in Utah. The majority of the San Juan River flows through a semi‑desert region covered with sparse vegetation and highly erosive soils that are formed mainly from sandstone and shale parent materials. Historically, the San Juan River has been a sandy, silt laden river. Personal journals and logs kept by early explorers, fur trappers, and settlers that ventured into the region mention the high levels of the sand and silt content of the San Juan River.

To date, studies have focused on historical flows and simulation of the natural hydrograph and its relationship to the survival of the Colorado squawfish and the razorback sucker, as well as heavy metals impacts and polynuclear aromatic hydrocarbon toxicity below the Navajo Dam. Bureau of Reclamation's water releases from Navajo Dam have been successful in simulating the natural hydrograph based on historical flow data prior to the construction of the dam. However, the quality of water used is different than pre‑dam era due to the reservoir's effects both on solids settling and chemical reactions. Investigations into the effects of silt and salt contents of the San Juan River water and its relationship to the survival and recovery of the Colorado squawfish and razorback sucker are non‑existent or un‑published. BLM feels that siltation differences and salinization differences may have changed the habitat and water quality characteristics that the species prefer. The effects of erosion below the dam may also appear more drastic since the dam was constructed because the upper sections of the San Juan, Piedra and the Los Pinos Rivers have been contained, with 30 miles of lake to settle their contents. They may, in fact, be more impacted due to road development in the San Juan Basin, but there is little to no documentation of sediment loading in the area.

Detailed need:

1.         Historical review of siltation and salinization of the San Juan River prior to construction of man made dams.

2.         Effects of silt and salt content of the San Juan River water and its relationship to the survival of the Colorado squawfish and razorback sucker.

3.         Effects of solids settling and chemical reactions due to reservoirs and their effect on the survival and recovery of the Colorado squawfish and razorback sucker.

4.        Impacts of road development in the San Juan Basin and their impact on sediment load in the area.

MANAGEMENT PROBLEM WITH NEED: To further the understanding of proposed and ongoing oil and gas leasing and development activities and the likelihood of  jeopardizing the survival and recovery of the Colorado squawfish and razorback sucker through the degradation of the aquatic habitat in the San Juan River. There is a general concern about the water quality and its impacts to the recovery of Colorado squawfish and razorback sucker, both endangered species.

BLM BUREAU CONTACTS:

Joel Farrell (505) 599-6310

Dale Wirth (505) 599-6320, dwirth@nm0151wp.nmso.nm.blm.gov)

BRD PRIMARY CENTER: Columbia Environmental Research Center (CERC)

BRD CENTER CONTACT: Susan Finger

RESULTS OF BRD-INITIATED COMMUNICATION (FY00):  Studies conducted on the San Juan River have resulted in a final completion report delivered to BLM, a Masters Thesis from New Mexico State Univeristy at Las Cruces, and numerous scientific presentations and posters at national meetings.  Scientists from CERC are working with the  extensive data set available from the San Juan Basin to evaluate the relative importance of multiple stressors in this river system.  Information from the completed thesis on benthic invertebrates suggests that habitat limitations in the system are a major factor influencing the densities of fish species including the endangered razorback suckers and Colorado squawfish.  In this study, benthic community composition and diversity increased when species were offered suitable habitat.  Lack of interstitial spaces in the substrate likely limit the success of benthic communities in this system.  This same degraded benthic habitat affects the fish populations indirectly through lack of available food and also limits the success of fish reproduction.  Further analysis of existing results is ongoing with the intention of developing a model incorporating chemical and physical characteristics of the San Juan Basin.

DATE SUBMITTED TO REGIONAL OFFICE: March 13, 2000

PREPARED BY:  Susan Finger and Ann Allert, Columbia Environmental Research Center

RESULTS OF BRD-INITIATED COMMUNICATION (FY99):  Studies in the San Juan Basin by BRD, BLM, and FWS have focused on historical flows and simulation of the natural hydrograph and its relationship to the survival of the Colorado squawfish and the razorback sucker, as well as potential toxicity of irrigation drainwater, heavy metals, and polynuclear aromatic hydrocarbons below the Navajo Dam.  BLM feels that siltation differences and salinization differences may have changed the habitat and water quality characteristics that the species prefer.  The effects of erosion below the dam may also appear more drastic since the dam was constructed  because the upper sections of the San Juan, Piedra and the Los Pinos Rivers have been contained, with 30 miles of lake to settle their contents. BRD has been in contact with BLM to discuss San Juan Basin issues in April, May, July, and August of 1998.  CERC has also presented information on BRD projects conducted in cooperation with BLM at several national meetings and most recently discussed the methods for interpreting the effects of salinity and siltation as two of many stressors affecting fisheries in that system.   CERC is using information from several studies conducted in this basin to evaluate the relative importance of different ecological factors on the success of razorback suckers and Colorado squawfish.  Issues associated with salinization in the San Juan River link directly to irrigation input.  Existing studies have documented increases in water salinity as the river moves downstream from Navajo Dam. Recently completed studies on benthic invertebrate communities are being used to evaluate the level of siltation in stretches of the river below Navajo Dam and determine the quality of the habitat.  Because of the many anthropogenic changes in this basin, it will be impossible to attribute reduced numbers of razorback suckers and Colorado squawfish to a single cause.  However, it may be possible to determine the relative importance of multiple stressors in determining population success.  ECRC has been involved in projects in the San Juan Basin since 1994.  Contacts with Joel Farrel and other BLM contacts will continue on a regular basis.

DATE SUBMITTED TO REGIONAL OFFICE: December 18,1998

PREPARED BY: Steve Hamilton and Susan Finger, Columbia Environmental Research Center

RESULTS OF BRD‑INITIATED COMMUNICATION (FY98):  BRD studies during the past three years have investigated the effects of potential oil and gas development on aquatic resources in the San Juan River. The final report is near completion and should be in the hands of BLM’s Farmington, NM office by March. Additional work has been completed on the effects of inorganic elements associated with irrigation practices on the flannelmouth sucker in the San Juan River. Both studies have investigated issues that relate to salinization in the San Juan River. Both studies have also shown increases in water salinity as the river moves downstream from Navajo Dam. Habitat quality which includes aspects of siltation has also been addressed in a separate study with information to be available within the year. Of the four detailed needs listed in this BIN, information is currently available for the potential effects of the salinity and associated contaminants on the survival of native fishes. Attempts will be made to identify resources to compile a historical review of siltation and salinization of the San Juan river prior to dams.

DATE SUBMITTED TO REGIONAL OFFICE: November 14, 1997

PREPARED BY: Steve Hamilton, Columbia Environmental Research Center, Field Research Station, Yankton, RR 1, Box 295, Yankton, SD 57078‑9214, 605‑665‑9217 and Susan Finger, Columbia Environmental Research Center, 4200 New Haven Road, Columbia, MO 65201, 573‑875‑5399 ext.1850

BUREAU OF LAND MANAGEMENT

BIN REPORT

TITLE:   Abandoned Mine Reclamation Pilot Initiative

SUBMITTING BUREAU:                Bureau of  Land Management

ORIGINATING OFFICE:    Montana State Office

BIN NUMBER:                                 BLM09CR98

BRD REGION:                                 Central

DESCRIPTION OF NEED:  Biologic Assessment and Monitoring of Priority Watersheds involved in Interdepartmental Abandoned Mine Land Initiative. Land management agencies require assessment of fisheries, macroinvertebrate, pheriphyton, etc, to determine the success of cleaning up abandoned mines and to target their clean-up efforts. The purpose of the biological assessment is to identify the source and movement of metals in key aquatic organisms, provide an assessment of exposure and health status of resident fish, and determine if exposure has resulted in a quantitative loss in fish populations in the Boulder River Basin. 

The aquatic studies are needed to define baseline conditions for metals loading in various aquatic communities and to determine the magnitude and pathways of exposure from mining waste activities.  Analysis of baseline and metals‑impacted streams will allow us the opportunity to determine the loss in quantity and health of the fishery resource and determine how this loss relates to metals exposure through various pathways. The recovery of fishery resources will be one of the gages by which we measure the success of remediation in the Boulder River Basin.

Integration of the biological tasks in this study with results of water and sediment analyses will allow assessment of the overall impact of metals on the Boulder River Basin. Interpretation of the results from the physical, chemical, and biological monitoring will establish a baseline for the basin and provide another gage by which we can measure the success of restoration on mining‑impacted areas.  The following represent tasks associated with this bureau need.

Task 1. Biological Pathways Assessment

Four samples each of biofilm, benthic macro invertebrates, and fish will be collected from 12 sites. Test sites will include upper and lower Basin Creek, upper and lower Cataract Creek, upper and lower High Ore Creek; and the Boulder River below Basin Creek, Cataract Creek, near Galena Gulch, and at the town of Boulder. Reference sites will include the Boulder River near Red Rock Creek and the Little Boulder River. Biofilm and benthic invertebrates will be collected from the river by standard procedures. Fish will be obtained from a hatchery source and held in live containers to assure the presence of fish at all sites and to provide consistency in size and species of fish analyzed. Samples will be analyzed by AA and/or ICP‑MS to determine the concentration of As, Cd, Cu, Pb, and Zn.

Task 2. Fish Population Assessments

A quantitative fish population analysis will be performed on three test and two reference sites. The test sites are thought to be impacted by mining wastes and to represent sites where metals contamination may be the major limiting factor to the fishery resource. The test sites include the Boulder River near Galena Gulch, lower Basin Creek, and lower Cataract Creek. Reference sites were selected according to their comparability to the test sites in valley and habitat type, stream gradient, pool-to-riffle ratio, and presence of like species and size of fish. The Boulder River near Red Rock Creek and the Little Boulder River were selected as reference sites and have no known impacts from mining.  The quantitative fish population analyses will be performed on 300-m sections of streams by standardized 3‑pass, mark and recapture or 2-3 pass depletion methods. Population analysis will determine fish species composition, abundance, and population structure. Physical habitat will be assessed at each site to assure that test and reference sites have equivalent habitat. Aquatic macroinvertebrates will be collected from each site by standard procedures to determine biotic integrity of the benthic community. A Hess sampler will be used to collect four samples at each site. Abundance and diversity of insect taxa will be measured for each sample and each site will be evaluated by using a metals-olerant index which was developed for the Clark Fork River. A qualitative fish assessment will be performed at additional sites including upper Catarak, and upper and lower High Ore Creek. This survey will be performed to determine the species and abundance of fish (catch per unit effort) present. Physical habitat assessments and analysis of the benthic community also will be performed at these sites.

Task 3. Fish Exposure and Health Status Assessment

Ten fish will be collected from each of the five sites in Task 2 to measure the exposure of selected target tissues to metals. Lipid peroxidation and metallothionein will be measured in the target tissues to associate fish health with metals exposure. The following fish tissues will be analyzed for metals exposure and health assessment: gill, kidney, liver, pyloric caeca, and intestine. Concentrations of As, Cd, Cu, Pb, and Zn will be determined in target tissues by AA and ICP‑MS. This information will help identify the source (water, diet, systemic) and amount of exposure. Measurements of metallothionein and lipid peroxidation will be determined on target tissues by standard procedures to determine if physiological impairment and tissue damage have occurred. These measures of health impairment will be compared to metals concentration to determine the health risk of the fish community. Metallothionein is a metal binding protein that is induced in certain tissues by metals such as Cd, Cu, and Zn. Formation of metallothionein is an energy consumptive process that results in reduced energy available for growth and maintenance. Lipid peroxidation is a process by which peroxides are formed with fatty acids in the cell membrane. Lipid peroxidation results in a loss of the integrity of the cell membrane and an inability of the cell to control its fluidity; this process can lead to cell and tissue death; metals are known to act as a catalyst in this process.

MANAGEMENT PROBLEM WITH NEED: Determine the improvement in beneficial use attainment (cold water aquatic life) from cleaning up abandoned mine lands on a watershed basis.

BLM BUREAU CONTACT: Tim Bozorth, (406) 255‑2794 email tbozorth@mt.blm.gov

BRD PRIMARY CENTER: Columbia Environmental Research Center (CERC) Fort Collins Science Center (MESC)

BRD CENTER CONTACT: Susan Finger (Lee Ischinger)

RESULTS OF BRD-INITIATED COMMUNICATION (FY00):  The AML Team has participated in numerous national meetings and workshops during the last year.  In addition, a session on Abandoned Mine Land issues was organized and presented at the 1999 DOI Conference on the Environment.  Work on this effort by the Columbia Environmental Research Center and the Fort Collins Science Center continues in both the Colorado and the Montana basins.  All field studies are completed in both basins and scientists are analyzing data and preparing project-specific final reports.  In the Montana watershed, whole bodies of fish had elevated concentrations of all metals but, Cd, Cu, and Pb, with metals most concentrated in liver and gill.  In fact, the fish gills accumulated similar concentrations of Cd as did the benthic invertebrates.  The elevated concentrations of metals were associated with depressed populations and sizes of fish.  For example, Cataract Creek had the smallest estimated fish populations, smallest sized fish, and the greatest metal concentrations.  In the Colorado watershed, USGS teams are currently defining sub-basins and working with BLM to define sites that will most likely result in meaningful restoration.  Information on the geology of the basin, sources and loading rates, and biological responses is being integrated to assist BLM in management decisions.  For both basins, all project-specific reports by all USGS disciplines will be completed this fiscal year.  A synthesis document describing each watershed will be prepared during the next fiscal year.  Project completion is currently scheduled for the end of FY2001.

DATE SUBMITTED TO REGIONAL OFFICE: March 13, 2000

PREPARED BY: Susan Finger, CERC, 573‑876‑1850

RESULTS OF BRD-INITIATED COMMUNICATION (FY99):  This BIN is currently being addressed by all four USGS divisions under the Abandoned Mine Lands Initiative (http://wwwrvares.er.usgs.gov/amli).  BRD studies are being conducted by CERC and MESC in Boulder River in Montana and in the Animas River in Colorado.  BRD is applying techniques to assess fish and invertebrate communities and their associated habitats in the areas impacted by historic mining activities to provide guidance to federal land management agencies for remediation of abandoned mine lands.  Work in support of this BIN is being conducted in cooperation with BLM and USFS.  A meeting of all participants including USGS, BLM, USFS, EPA, state and private groups, was held February 3-5 in Denver.  A published proceedings is now available from this meeting.  Scientists from CERC and MESC actively participate in discussions with BLM representatives in Colorado (Stephanie O’dell) and Montana (Tim Bozorth) on a regular basis.  FY99 funding for work on Abandoned Mine Lands is being used to address unfunded priority issues in each watershed.  Major studies on-going in Colorado and Montana include assessment of fish health and measures of biological injury, on-site toxicity assessments with trout, evaluation of sediment toxicity, determination of habitat suitability for fish reproductive success, quantification of pathways of metals exposures, and evaluation of the impacts of episodic acidic events resulting from snowmelt or heavy runoff events.  Summaries of all these projects as well as other studies being conducted by USGS have been provided to BLM. 

DATE SUBMITTED TO REGIONAL OFFICE: December 18

PREPARED BY: Susan Finger, Columbia Environmental Research Center, 4200 New Haven Road, Columbia, MO 65201, 573‑876‑1850

RESULTS OF BRD‑INITIATED COMMUNICATION (FY98): This BIN is currently being addressed by all four USGS divisions under the Abandoned Mine Lands Initiative (http://wwwrvares.er.usgs.gov/amli). BRD studies are being conducted by CERC and MESC in Boulder Creek in Montana and in the Animas River in Colorado. BRD is applying techniques to assess fish and invertebrate communities and their associated habitats in the areas impacted by historic mining activities to provide guidance to federal land management agencies for remediation of abandoned mine lands. Work in support of this BIN is being conducted in cooperation with BLM and USFS. A meeting of all participants including USGS, BLM, USFS, EPA, state and private groups, is scheduled for February 3‑5 in Denver.

DATE SUBMITTED TO REGIONAL OFFICE: November 14, 1997

PREPARED BY: Susan Finger, Columbia Environmental Research Contaminant, 4200 New Haven Road, Columbia, MO 65201, 573-876-1850

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