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Completing the SF Bay Mercury TMDL Carrie Austin SF Bay Water Board.

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Presentation on theme: "Completing the SF Bay Mercury TMDL Carrie Austin SF Bay Water Board."— Presentation transcript:

1 Completing the SF Bay Mercury TMDL Carrie Austin SF Bay Water Board

2 2 Overview of Water Board Response More Stringent Requirements for Wastewater More Stringent Requirements for Wastewater New Water Quality Objectives New Water Quality Objectives Actions to clarify and improve implementation Actions to clarify and improve implementation

3 3 Mercury Loads and Allocations SOURCE CATEGORY EXISTING LOAD (kg/yr) ALLOCATION (kg/yr) Bed Erosion 460220 Central Valley Watershed 440330 Urban Runoff 16082 Guadalupe River Mining Legacy 922 Atmospheric Deposition 2727 Rural Runoff 2525 Wastewater20 20  14? Dredging and Disposal net loss net loss 0  ambient concentration TOTAL1,220 706  700?

4 4 Wastewater [Hg] T “Trigger” Standard NPDES permit calculation Standard NPDES permit calculation Performance based: Mean + 3 SDs Performance based: Mean + 3 SDs About 99 th percentile About 99 th percentile Triggers for “advanced” & “secondary” Triggers for “advanced” & “secondary”

5 5 Wastewater Individual WLAs Calculated differently Calculated differently Performance-based Performance-based 99% UCL on the Mean 99% UCL on the Mean Sum of Individual WLAs = “group trigger” Sum of Individual WLAs = “group trigger”

6 6 Revised Wastewater Allocations Municipal advanced -20% Municipal secondary -40% Industrial3? Analysis pending Total2014? Current allocations (kg/year) Revised allocations 17 11? 99% UCL on the mean = 20 kg/yr annual average

7 7 New Water Quality Objectives Vacate water column objective 0.025 ug/L 4-day average Vacate water column objective 0.025 ug/L 4-day average Establish two new fish tissue objectives: 0.2 ppm larger fish 0.03 ppm smaller prey fish Establish two new fish tissue objectives: 0.2 ppm larger fish 0.03 ppm smaller prey fish Second fish tissue objectives in California – Clear Lake was first.

8 8 Timeline and Next Steps Release documents for public review mid-March Release documents for public review mid-March Public review period through April Public review period through April Water Board action in June Water Board action in June

9 9 Guadalupe River Watershed Mercury TMDL Carrie Austin SF Bay Water Board

10 10 Debut: GRW Hg TMDL Public Comment period closes 06/30/06 Documents available from: http://www.waterboards.ca.gov/sanfrancisco bay/guadaluperivermercurytmdl.htm http://www.waterboards.ca.gov/sanfrancisco bay/guadaluperivermercurytmdl.htm  TMDL Project Report Jan06  Final Conceptual Model Report May05  Derivation Numeric Wildlife Targets Apr05

11 11 TMDL Overview  Problem  Sources  Targets  Allocations  Implementation

12 12 Citation: Figure 3-25 Final Conceptual Model Report (Tetra Tech 2005c) Problem: Bioaccumulation Summary of 2004 Fish Sampling Results

13 13 Citation: figure by Tetra Tech Sources Mining Waste Mining Waste Urban Runoff Urban Runoff Atmospheric Deposition Atmospheric Deposition Natural Hg in soil Natural Hg in soil

14 14 Mining Waste Erodes into: Predominantly Alamitos Creek & Lake Almaden Canal from Almaden  Calero Reservoir Jacques Gulch into Almaden Reservoir Small area into Guadalupe Reservoir Remainder into Guadalupe Creek

15 15 TARGETS

16 16 Numeric Targets = “Fishable” Table 5.3 Fish Targets (ppm methylmercury, wet weight) Protection of Wildlife Protection of Human Health TL3 Fish 50 – 150 mm TL3 Fish 150 – 350 mm Typical Size and Species of Fish Consumed 0.05 ppm0.10 ppm0.3 ppm USFWS calculation USEPA MeHg criterion

17 17 Achievable Targets  Ore – underground Cinnabar outcrops on Mine Hill Cinnabar outcrops on Mine Hill Cinnabar nuggets in Deep Gulch Cinnabar nuggets in Deep Gulch  No deep lakes Hypothesis: low mercury bioaccumulation pre-mining

18 18 ALLOCATIONS

19 19 “Impoundments” Impoundments are engineered structures that pond water. dams (i.e., reservoirs and artificial lakes), dams (i.e., reservoirs and artificial lakes), flood control structures, flood control structures, other engineered features (such as drop structures), and other engineered features (such as drop structures), and non-native invasive vegetation that ponds water non-native invasive vegetation that ponds water

20 20 Fish in Reference Reservoir Fishable: 40-cm Largemouth bass: 0.6 ppm < 0.66 ppm TL4 human health target 40-cm Largemouth bass: 0.6 ppm < 0.66 ppm TL4 human health target Age-1 Largemouth bass: 0.09 ppm @ 89 mm length, equals 0.045 in TL3 < 0.05 ppm wildlife target Age-1 Largemouth bass: 0.09 ppm @ 89 mm length, equals 0.045 in TL3 < 0.05 ppm wildlife target

21 21 Allocation: Hypolimnion MeHg

22 22 Downstream Implications Figure 6.7 Dissolved Methylmercury Below Reservoirs, July 2003 Citation: Figure 5-10 Final Conceptual Model Report (Tetra Tech 2005)

23 23 Lower [Hg] sed  Lower [Hg] fish

24 24 Allocations based on Reference Reservoir Impoundment Methylmercury Allocation  3.0 ng/l (parts per trillion) MeHg seasonal maximum in the hypolimnion  3.0 ng/l (parts per trillion) MeHg seasonal maximum in the hypolimnion of 3 reservoirs and Almaden Lake Mining Waste Total Mercury Allocations  0.1 ppm mercury (annual median, dry weight) in erodable soil finestransported  0.1 ppm mercury (annual median, dry weight) in erodable soil fines transported from the New Almaden Mining District  (see report regarding 0.2 ppm mercury)

25 25 IMPLEMENTATION

26 26 Start in Headwaters: New Almaden 0.1 ppm mercury in erodable soil fines transportedin runoff 0.1 ppm mercury in erodable soil fines transported in runoff BMPs for erosion control w/in 10 yrs

27 27 Impoundment MeHg Production Thermal stratification (natural, good) Low DO in hypolimnion SRB produce HS - which dissolves mining waste SRB produce MeHg

28 28 Is Oxygen the Solution to MeHg? Thermal stratification (natural, good) oxygenated oxygenated hypolimnion

29 29 Dissolved Hg Hypotheses  Wet season: HgDiss transported in storm water from mining waste quickly attaches to particulates; erosion control sufficient.  Dry season: main concern with HgDiss is dry season dissolution of mining waste under anoxic conditions

30 30 Summary Figure S-1 Solving the Mercury Problem Citation: figure prepared by Tetra Tech

31 31 Comments on Guad Hg TMDL Public Comment period ends June 30 send to: Carrie Austin SF Bay Water Board 1515 Clay Street, #1400 Oakland, CA 94612 caustin@waterboards.ca.gov


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