Difference between revisions of "WATER QUALITY"

• 2017 Water Quality PEP Agenda
• 2017 Water Quality PEP Prospectus

Reading List

Adaptive Management

• Melis et al. 2015. Surprise and Opportunity for Learning in Grand Canyon: the Glen Canyon Dam Adaptive Management Program. Ecology and Society 20(3):22.

Calcite Coprecipitation

• Cohen et al. 2013. Diel phosphorus variation and the stoichiometry of ecosystem metabolism in a large spring-fed river. Ecological Monographs, Vol. 83, No. 2 (May 2013), pp. 155-176
• Corman et al. 2015. Stoichiometric impact of calcium carbonate deposition on nitrogen and phosphorus supplies in three montane streams. Biogeochemistry.
• Corman et al. 2016. Calcium carbonate deposition drives nutrient cycling in a calcareous headwater stream. Ecological Monographs, 86(4), 2016, pp. 448–461
• Hamilton et al. 2008. Biogenic calcite–phosphorus precipitation as a negative feedback to lake eutrophication. Can. J. Fish. Aquat. Sci. 66: 343–350
• Otsuki and Wtzel. 1972. Coprecipitation of phosphate with carbonates in a marl lake.
• Reynolds and Johnson. 1974. Major element geochemistry of Lake Powell. Lake Powell Research Project Bulletin #5.
• Reynolds. 1978. Polyphenol inhibition of calcite precipitation in Lake Powell. Limnol. Oceanogr., 23(4), 1978, 585-597.

CE-QUAL Modeling

• ERM’s review of the Lake Powell CE-QUAL-W2 Model
• Williams, N.T., 2007, Modeling dissolved oxygen in Lake Powell using CE-QUAL-W2: Provo, Brigham Young University, thesis.
• Williams, N.T., 2007, Projecting Temperature in Lake Powell and the Glen Canyon Dam Tailrace. Proceedings of the Colorado River Basin Science and Resource Management Symposium

Contaminants

• Hart et al. 2005. Physical and chemical characteristics of Knowles, Forgotten, and Moqui Canyons, and effects of recreational use on water quality, Lake Powell, Arizona and Utah: U.S. Geological Survey Scientific Investigations Report 2004–5120, 43 p.
• Schonauer. 2014. The presence and distribution of polycyclic aromatic hydrocarbons and inorganic elements in water and lakebed materials and the potential for bioconcentration in biota at established sampling sites on Lake Powell, Utah and Arizona: U.S. Geological Survey Open-File Report 2013–1299, 28 p.
• Waddell and Wiens. 1993. Reconnaissance study of trace elements in water, sediment, and biota of Lake Powell.
• Walters. 2015. Mercury and selenium accumulation in the Colorado River food web, Grand Canyon, USA. Environmental Toxicology and Chemistry, Vol. 34, No. 10, pp. 2385–2394, 2015

General Lake Powell Limnology

• Gloss. 1980. Advective control of nutrient dynamics in the epilimnion of a large reservoir. Limnol. Oceanogr., 25(2), 1980, 219-228
• Johnson and Page. 1981. Oxygen depleted waters: Origin and distribution in Lake Powell, Utah - Arizona. Proceedings of the Symposium on surface water impediments. American Society of Civil Engineers, NY.
• Johnson and Merritt. 1979. Convective and Advective Circulation of Lake Powell, Utah-Arizona, During 1972-1975. Water Resources Research. 15:4
• Stanford and Ward. 1990. Limnology of Lake Powell and the Chemistry of the Colorado River. Colorado River Ecology and Dam Management: Proceedings of a Symposium May 24-25, 1990 Santa Fe, New Mexico. Chap 5.
• Wildman and Vernieu. 2017. Turbid releases from Glen Canyon Dam, Arizona, following rainfall-runoff events of September 2013, Lake and Reservoir Management

Long-term Water Quality Trends

• Kelly 2001. Influence of reservoirs on solute transport: A regional-scale approach. Hydrol. Process. 15, 1227–1249
• Stets. 2014. Long-term trends in alkalinity in large rivers of the conterminous US in relation to acidification, agriculture, and hydrologic modification. Sci Total Environ. 2014 Aug 1;488-489:280-9

P Biogeochemistry

• Wildman et al. 2011. Physical, Chemical, and Mineralogical Characteristics of a Reservoir Sediment Delta (Lake Powell, USA) and Implications for Water Quality during Low Water Level. J Environ Qual. 2011 Mar-Apr;40(2):575-86.
• Bostrom et al. 1988. Exchange of phosphorus across the sediment-water interface. Hydrobiologia 170: 229-244
• Hering and Wildman. A study of the dynamics of phosphorus associated with suspended and deposited sediments in the Colorado River delta, Lake Powell, Utah.
• Kinsman-Costello et al. 2014. Re-flooding a Historically Drained Wetland Leads to Rapid Sediment Phosphorus Release. Ecosystems 17: 641–656
• Kinsman-Costello et al. 2016. Phosphorus release from the drying and reflooding of diverse shallow sediments
• Mayer and Gloss. 1980. Buffering of silica and phosphate in a turbid river. Limnol. Oceanogr., 25(l), 12-22
• Wildman and Hering. 2011. Potential for release of sediment phosphorus to Lake Powell (Utah and Arizona) due to sediment resuspension during low water level. Lake and Reservoir Management, 27:4, 365-375

USGS Data Series, Circulars, and other Reports

• GCDAMP FY 2017 Knowledge Assessment: Final Report from the Executive Coordinator for the Science Advisors Program
• Glen Canyon Dam Adaptive Management Program Triennial Budget and Work Plan— Fiscal Years 2018–2020
• USGS Workshop on Scientific Aspects of a Long-Term Experimental Plan for Glen Canyon Dam, April 10–11, 2007, Flagstaff, Arizona
• Final report of the 2001 Protocol Evaluation Panel for the Grand Canyon Monitoring and Research Center Integrated Water Quality Program (IWQP)
• Historical Physical and Chemical Data for Water in Lake Powell and from Glen Canyon Dam Releases, Utah-Arizona, 1964–2013
• The State of the Colorado River Ecosystem in Grand Canyon: A report of the Grand Canyon Monitoring and Research Center 1991-2004
• Biological Data for Water in Lake Powell and from Glen Canyon Dam Releases, Utah and Arizona, 1990–2009

Water Quality and Glen Canyon Dam Management

• Hueftle and Stevens. 2001. Experimental flood effects on the limnology of Lake Powell Reservoir, Southwestern USA. Ecological Applications, 11(3), pp. 644–656
• Effects of the 2008 High-Flow Experiment on Water Quality in Lake Powell and Glen Canyon Dam Releases, Utah-Arizona

Water Quality and Metabolism in the Colorado River below Glen Canyon Dam

• Water quality investigation of seventeen Grand Canyon tributaries: July 2004 - May 2005
• Hall et al. 2015. Turbidity, light, temperature, and hydropeaking control primary productivity in the Colorado River, Grand Canyon. Limnol. Oceanogr. 60, 512–526
• Hall et al. 2012. Air–water oxygen exchange in a large whitewater river. Limnology and Oceanography: Fluids and Environments
• Larned et al. 2004. Mass-transfer–limited nitrogen and phosphorus uptake by stream periphyton: A conceptual model and experimental evidence. Limnol. Oceanogr., 49(6), 1992–2000
• Payn et al. 2017. A coupled metabolic-hydraulic model and calibration scheme for estimating whole-river metabolism during dynamic flow conditions. Limnol. Oceanogr.

• Nutrients Page

• Colorado River at Lees Ferry
• Colorado River at 30 mile
• Colorado River above LCR
• Bright Angel Creek
• Colorado River abv National Canyon
• Colorado River bl Diamond Creek

2017

• Payn et al., 2017, A coupled metabolic-hydraulic model and calibration scheme for estimating of whole-river metabolism during dynamic flow conditions: Limnology and Oceanography: Methods, v.15, no.10, p. 847-866
• Bernhardt et al. 2017. The metabolic regimes of flowing waters: Limnology and Oceanography
• Water Quality in Lake Powell and Its Influence on the Colorado River Below Glen Canyon Dam PPT

2016

• Voichick et al. 2016. Water clarity of the Colorado River—Implications for food webs and fish communities: U.S. Geological Survey Fact Sheet 2016–3053, 4 p.
• Project 2: Streamflow, Water Quality, Sediment Transport, and Sand Budgets in the Colorado River Ecosystem

2015

• Historical Physical and Chemical Data for Water in Lake Powell and from Glen Canyon Dam Releases, Utah-Arizona, 1964–2013
• Water Quality in Lake Mead and Upstream Influences: Dissolved Oxygen during 2014
• Streamflow, Water Quality, and Sediment Transport in the Colorado River Ecosystem
• Glen Canyon Physical Environment Update – Water Quality, Tributary Influences & Channel Analyses & Flows

2014

• How the 2014 HFE affected water quality parameters such as dissolved oxygen (DO) and temperature below Glen Canyon Dam.

2012

• Integrated Quality-of-Water Monitoring
• Flow Temp Turbidity

2010

• Effects of Drought on Water Quality of Lake Powell and Glen Canyon Dam Releases
• Update on Water Quality and 2010 Sand Input

2006

• Update on Water Quality of Lake Powell and Glen Canyon Dam Releases

2005

• Reclamation to continue experimental operations at Glen Canyon Dam; Efforts address low dissolved oxygen levels below dam

• Final report of the 2001 Protocol Evaluation Panel for the Grand Canyon Monitoring and Research Center Integrated Water Quality Program (IWQP)

Rough operation of the turbines

Increases the oxygenation of water going through the power plant Is damaging to the turbines

• Reclamation to continue experimental operations at Glen Canyon Dam to increase dissolved oxygen (2005)

Oxygenation of the tailwater using the bypass tubes

The Basin States have maintained that according to Sec 602a of the Colorado River Basin Project Act (1968), the bypass tubes at Glen Canyon Dam can only be used to avoid anticipated spills from Lake Powell. The Basin States have agreed to bypass at Glen Canyon Dam for HFEs on the condition that it be done as part of an experiment and not a management action or operational decision. Costs associated with any release that bypasses the powerplant for reasons other than to avoid a spill or for experimentation relating to HFEs would have to be borne by the GCDAMP (see DOI determination for costs of the 2004 BHBF).

Adding power generation to the bypass tubes

Allows for drawing water from deeper in Lake Powell where colder and more oxygenated water may be present.

• Generation at Outlet Glen Canyon Dam Plan of Study CRSP Power Peaking Capacity (March 1981)

Other methods:

• Forebay diffusers
• Side stream super-saturation
• Aeration
• Turbine venting
• Surface water pumps (impellers)

(Mobley Engineering: Hydropower Enhancement Technologies)