Concerns about the Current Approach to Nutrient Criteria.

Slides:



Advertisements
Similar presentations
Ann D Hirekatur Project Manager State of Lake Wisconsin Meeting July 13, 2013 Wisconsin River Basin Water Quality Improvement Project.
Advertisements

Presented to: Reitz Lake Open House July 12, 2005 Randy Anhorn Principle Environmental Scientist Metropolitan Council Environmental Services
Periphyton Data from National-Scale Assessments Can Inform Nutrient Criteria Development for Southeastern States R. Jan Stevenson Michigan State University.
Public Meeting: March 3, 2014 Truckee River Water Quality Standards Review.
RICE CREEK CHAIN OF LAKES TMDL. PELTIER LAKE TOTAL PHOSPHORUS MONITORING DATA.
Lakes of Missouri Volunteer Program University of Missouri-Columbia The Missouri’s Lakes and Reservoirs The Missouri Department of Natural Resources Region.
Water Quality Standards Section Water Permits Division Office of Environmental Services Louisiana Department of Environmental Quality December 2, 2010.
Prioritization Workgroup Summary. Workgroup Topics Nutrient results What is a watershed? What is a TMDL? Prioritization methods Basin framework and management.
Agricultural Phosphorus and Eutrophication by Don Pitts Agricultural Engineer & Water Quality Specialist USDA, NRCS Champaign, IL.
Traditionally relied on MWI Random transect aerial survey –Reinecke et al. (1990) –Pearse et al. (2005) –State agencies continuing work MDWFP (2005-present)
Limnology 101 Dan Obrecht MU Limnology
Team Meeting #5, Great Lakes Protection Fund Grant A Phosphorus Soil Test Metric To Reduce Dissolved Phosphorus Loading to Lake Erie Heidelberg University.
Evaluation of Volunteer Data – The Lakes of Missouri Volunteer Program Review Daniel V. Obrecht Anthony P. Thorpe John R. Jones Department of Fisheries.
©2010 Elsevier, Inc. Chapter 18 Trophic State and Eutrophication Dodds & Whiles.
New Hampshire Estuaries Project September 30, 2005 Estuarine Nutrient Criteria Presentation to New Hampshire Estuaries Project Technical Advisory Committee.
Purposes and Ideas Behind the Project Esau – I have a interest in a career that involves natural resources. Austin – I am a new student at Wildlands this.
1 The ABC’s of Water in Arizona A general understanding of water and the Hydrologic Cycle is necessary to have basis for unlocking more complex topics.
Developing Nutrient Criteria – Divide and Conquer! Dan Obrecht, MU Limnology.
Justification of Review of Water Quality Standards for Nutrients and other Constituents Randy Pahl, NDEP.
Missouri Nutrient Criteria Plan Mark Osborn October 20, 2005.
NYCDEP Evaluation of Watershed Management Programs FAD requirement: Last one ; Next FAD Assessment : Use models to evaluate effects.
Model Application for WQS Review Process December 14, 2011 Laura Weintraub.
Pomme de Terre Lake Water Quality Summary Pomme de Terre Lake Water Quality Summary US Army Corps of Engineers Environmental Resources Section.
CE 374K Hydrology Frequency Factors. Frequency Analysis using Frequency Factors f(x) x xTxT.
Nutrient Benchmark Development Gary Welker, Ph.D. USEPA Region 7 Environmental Services Division.
Many times in statistical analysis, we do not know the TRUE mean of a population of interest. This is why we use sampling to be able to generalize the.
Water Chemistry By Lucas Kirby, Cynthia Watson, Meghan Dye and Stephanie Johnson.
Chapter 15 Data Analysis: Testing for Significant Differences.
2014 Dissolved Oxygen Assessment CHRP Meeting December 17, 2014 Heather Stoffel.
©2010 Elsevier, Inc. Chapter 17 Nutrient Use and Remineralization Dodds & Whiles.
Nutrient Criteria for the plains regions of Missouri.
What is a Border? Missouri’s Location Missouri is one of 12 states in the Midwest region of the United States. Eight states share borders with Missouri.
Water Quality Short Course April 11, 2007 Lake and Reservoir Dynamics Dan Obrecht – UMC
Secondary Site Locations on Large Reservoirs Issue 1 – How to select tributary arms for criteria monitoring Missouri’s large reservoirs are highly dendritic.
Proposed Nutrient Criteria for NH’s Estuaries Philip Trowbridge, P.E. NH Estuaries Project / NH DES November 17, 2008.
September 9-15, What happened? Over a 7 day period, a record amount of rain fell over the Front Range region of Northern Colorado As a result, rivers.
Delaware River Basin SPARROW Model Mary Chepiga, , Susan Colarullo, , Jeff Fischer, ,
Invest Nutrient Retention model Yonas Ghile.
Nutrient and Sulfide Export From a Mine Drainage Passive Treatment System S.A. Yepez & R.W. Nairn 29 th Annual Meeting of the American Society of Mining.
Hydrology of Colorado Water By Travis Hoesli. Hydrology of Colorado Unit Learning Objectives Recognize the Hydrologic Cycle that affects Colorado Water.
Response of benthic algae communities to nutrient enrichment in agricultural streams: Implications for establishing nutrient criteria R.W. Black 1, P.W.
Sentinel Lakes 2008 Zooplankton Update. Field Sampling MPCA staff collected 363 zooplankton samples. All 24 lakes were sampled monthly from April/May.
Reservoir and Lake Nutrient Criteria A Different Approach D.V. Obrecht, J.R. Jones & M.K. Knowlton – MU Limnology.
PHOSPHATE IN LAKES AND STREAMS
Adem.alabama.gov ADEM’s Monitoring Summary Reports Alabama – Tombigbee CWP Stakeholders Meeting Montgomery, Alabama 3 February 2010 Lisa Huff – ADEM Field.
By: Mrs. Jackson Tennessee Landforms There are many landforms in Tennessee. Landforms can affect the way we live and play. Let’s take a tour of Tennessee.
Watershed and water quality assessment of the Allen’s Creek watershed David A. Tomasko, Ph.D. Cheryl Propst, M.S. May 16, 2012.
Sustaining Lakes in a Changing Environment - SLICE.
Topics The Cart The Horse Answers to previously asked questions and comments on the comments to said questions Dan Obrecht – University of Missouri.
Abstract Man-made dams influence more than just the flow of water in a river. The build up of sediments and organic matter, increased residence times,
WATERSHEDS Concepts and Curriculum Review LAKE MONITORING AND ANALYSIS Tony Thorpe and Dan Obrecht Lakes of Missouri Volunteer Program – Univ. of Missouri.
Aquatic Ecosystem Overview: We need to understand the physical (e.g. hydrodynamics) and chemical environment that ultimately control the productivity,
Follow Up from the last Nutrient Criteria Meeting Dan Obrecht – UMC Limnology.
Nutrient Criteria for Reservoirs – A Review of Missouri’s Proposed Approach Daniel V. Obrecht Dept. of Fisheries and Wildlife Sciences University of Missouri.
Comparison of freshwater nutrient boundary values Geoff Phillips 1 & Jo-Anne Pitt 2 1 University of Stirling & University College London 2 Environment.
FW364 Ecological Problem Solving Residence Time of the Seas Mass Balance.
Measures of Variation. Variation Variation describes how widely data values are spread out about the center of a distribution.
GREAT BAY and NEW HAMPSHIRE WATER QUALITY STANDARDS
2016 Water Quality Assessment Update (thru Sep. 2016)
Aquatic Ecosystem Overview:
Shirley Birosik Environmental Specialist
Hydrology of Colorado Water
Nutrient Benchmark Development
Public Meeting February 19, 2009
Debra S. Baker and Donald G. Huggins
Total Phosphorus in Large Reservoirs
Lakes of Missouri Volunteer Program
Missouri Nutrient Criteria Development
Where is the earths water?
LARGE RESERVOIRS (and LMVP sites, in no particular order)
Presentation transcript:

Concerns about the Current Approach to Nutrient Criteria

GROUPCriteria A1-7 Large Ozark ReservoirsTP & CHL B Big River LakesTN & CHL C1 Plains FR<.4TP & CHL C2 Plains FR.4 -.6TP & CHL C3 Plains FR >.6TP D1 St. FrancoisTP D2 Ozark HighlandTP D3 Oz Border & PlateauTP

Current Approach for Large Ozark Reservoirs Median and 75 th percentile of chlorophyll values from each individual reservoir were used to set Assessment and Action Levels for that reservoir. Phosphorus Assessment and Action Levels were then back-calculated from the chlorophyll values.

Problems with this approach 1) Using historic data from an individual reservoir to set criteria for that reservoir = Status Quo 2) Each reservoir ends up with different Assessment and Action Levels, a different range of values that make up the Assessment range, and A/A Levels fall in different places along the distribution of data 3) Currently no rationale given for this approach

GROUPCriteria A1-7 Large Ozark ReservoirsTP & CHL B Big River LakesTN & CHL C1 Plains FR<.4TP & CHL C2 Plains FR.4 -.6TP & CHL C3 Plains FR >.6TP D1 St. FrancoisTP D2 Ozark HighlandTP D3 Oz Border & PlateauTP

Current Approach for Big River Lakes TN instead of TP criteria because the N:P ratios are generally low. Chlorophyll Assessment and Action Levels set at 25 and 65/90ug/L TN Assessment and Action Levels back- calculated from chlorophyll.

Problems with this approach 1) Low N:P may be misleading as some phosphorus is bound to NVSS and not readily available for uptake. 2) Light limitation of algae is likely in these lakes, weakening the Chlorophyll - nutrient relationship. 3) No mention of where the chlorophyll assessment and action levels come from in rationale.

GROUPCriteria A1-7 Large Ozark ReservoirsTP & CHL B Big River LakesTN & CHL C1 Plains FR<.4TP & CHL C2 Plains FR.4 -.6TP & CHL C3 Plains FR >.6TP D1 St. FrancoisTP D2 Ozark HighlandTP D3 Oz Border & PlateauTP

Current Approach for Plains Reservoirs with low flushing rates Chlorophyll Assessment Levels for each group are based on median values from two reference reservoirs, while Action Levels are set at 20 and 25 ug/L chlorophyll. Phosphorus Assessment and Action Levels are then back-calculated from the chlorophyll values.

Problem 1 – Misuse of the reference approach

Lake 10 mean Lake 9 mean Lake 8 mean Lake 7 mean Lake 6 mean Lake 5 mean Lake 4 mean Lake 3 mean Lake 2 mean Lake 1 mean Difference in data associated with differences in waterbodies (i.e. disturbances in watershed, hydrology, etc.) EPA Reference Approach 75% Approach looks at the range of values found in reference lakes.

Reservoir X value 10 value 9 value 8 value 7 value 6 value 5 value 4 value 3 value 2 value 1 Difference in data associated with climate and timing of sample collection Missouri’s Version 75% More rain Less rain Approach looks at the range of values found in two reference reservoirs.

A data set made up of individual values from one or two reservoirs is not the same as a data set containing mean values from multiple waterbodies!

Problem 2 – Use of reservoirs with forested watersheds as reference for reservoirs built in prairie landscape is inappropriate.

The 10% of Plains reservoirs with lowest TP concentrations (<22 ug/L) Rest of Plains reservoirs (TP >22 ug/L)

Proportion of watershed that is forest in “reference” reservoirs: Lincoln – 84% Forest – 67% Deer Ridge – 54% Nehai Tonkeia – 49%

Problem 3 – Action Levels of Unknown Origin Currently the rationale states that the chlorophyll action levels are based on: literature values (no citations) BPJ (whose?) examination of data set (?)

GROUPCriteria A1-7 Large Ozark ReservoirsTP & CHL B Big River LakesTN & CHL C1 Plains FR<.4TP & CHL C2 Plains FR.4 -.6TP & CHL C3 Plains FR >.6TP D1 St. FrancoisTP D2 Ozark HighlandTP D3 Oz Border & PlateauTP

Current Approach for Plains Reservoirs with high flushing rates Assessment and Action Levels are based on the Phosphorus-Flushing Rate relationship. Assessment Level is based on regression line (~50% of reservoirs above, ~50% below). The Action Level is set at alpha = 0.05 (about 5% of reservoirs in data set will be above the line).

Problem with this approach 1) The stakeholders group has not really discussed where the Assessment and Action Levels should be. These lines can be placed anywhere within the relation by changing the alpha value.

GROUPCriteria A1-7 Large Ozark ReservoirsTP & CHL B Big River LakesTN & CHL C1 Plains FR<.4TP & CHL C2 Plains FR.4 -.6TP & CHL C3 Plains FR >.6TP D1 St. FrancoisTP D2 Ozark HighlandTP D3 Oz Border & PlateauTP

Current Approach for smaller Ozark reservoirs Sub-regional approach, with different regions being held to oligotrophic, mesotrophic or eutrophic conditions based on “hydrology and geology.”

Are the differences in water quality related to hydrology and geology? Sub-RegionTPFRForestCropGrass St. Francois (oligo) %0.4%15% Ozark Highlands (meso) %0.8%17% Border/Plateau (eutro) %7.4%29%

Problem with this approach 1) Differences in water quality may be related to land-cover and not “regional hydrology and geology”

Level of Concern over the Current Matrix GROUP A 1-7 Large Ozark Reservoirs B Big River Lakes B Big River Lakes C1 Plains FR<.4 C2 Plains FR C3 Plains FR >.6 D1 St. Francois D2 Ozark Highland D3 Ozark Border & Plateau

Lake Woodrail – Columbia, MO Horizontal lines represent Assessment and Action Levels for C1 lakes.

YearTP (ug/L) Overall Average18 Lake Woodrail – Columbia, MO Summertime means (mid-May to mid-August)

Lake Woodrail – Columbia, MO

Symbols represent individual values, lines are current Assessment and Action Levels

Symbols represent annual geometric means, lines are current Assessment and Action Levels

Symbols represent individual values, lines are current Assessment and Action Levels

Symbols represent annual geometric means, lines are current Assessment and Action Levels

Symbols represent individual values, lines are current Assessment and Action Levels

Symbols represent annual geometric means, lines are current Assessment and Action Levels

Symbols represent individual values, lines are current Assessment and Action Levels

Symbols represent annual geometric means, lines are current Assessment and Action Levels

Above Above Assessment Action Pomme de Terre Individual Values TP46%22% CHL49%27% Annual ValuesTP50%17% CHL50%17% Stockton Individual ValuesTP38%11% CHL49%26% Annual ValuesTP33%6% CHL17%11%

Above Above Assessment Action Wappapello Individual Values TP32%12% CHL43%25% Annual ValuesTP29% 0% CHL35% 6% Clearwater Individual ValuesTP61%12% CHL50%25% Annual ValuesTP53%12% CHL59% 6%

Above Above Assessment Action Table Rock Individual Values TP74%37% CHL56%26% Annual ValuesTP79%32% CHL63%16% Lake of the Ozarks Individual ValuesTP56%39% CHL52%22% Annual ValuesTP65%40% CHL50%15%