Title: Middle Fork Project AQ 11
1Middle Fork ProjectAQ 11 Water Quality
Technical Study Plan Report Overview
2Water Quality Study Objectives and Related
Study Elements and Reports
Study Objective Characterize physical, chemical,
and bacterial water quality conditions in the
bypass reaches and the peaking reach, comparison
reaches, and Project reservoirs and diversion
pools and compare to the CVRWQCB Basin Plan
objectives and water quality standards.
Complete 2007 Water Quality Field Program
Conduct Voluntary Enhanced Water Quality Sampling
Conduct in-situ Field Measurement Sampling
Conduct General Water Quality Sampling
Conduct Coliform Sampling
Conduct Fish Tissue Analysis
Document 2007 Water Quality Sampling Results in
this report
Consult with Aquatic TWG
Determine if Additional Water Quality Sampling is
Needed
Determine if Additional Fish Tissue Analyses are
Needed
Determine if Additional Water Quality Sampling is
Needed to Address any Macroinvertebrate Issues
Develop Recommendations and Prepare Contingency
Studies, if necessary
Complete 2008 Contingency Water Quality Field
Program, if necessary
Document 2008 Water Quality Sampling Results in
Water Quality Report (2009), if necessary
3Study Objectives
- Characterize physical, chemical, and bacterial
water quality conditions in the bypass reaches
and the peaking reach, comparison reaches, and
Project reservoirs and diversion pools. - Compare water quality conditions to the Central
Valley Regional Water Quality Control Board
(CVRWQCB 1998) Basin Plan objectives and water
quality objectives.
4Existing Water Quality Objectives
- Water quality analytical results were compared
to - The Sacramento River Basin and San Joaquin River
Basin Plan Water Quality Control Plan (Basin
Plan) - California Toxics Rule (CTR)
- National Toxics Rule (NTR)
- Fish tissue analysis results were compared to
- Californias Office of Environmental Health and
Hazard Assessment (OEHHA) guidelines
5Potential Contingency Studies
- Additional Water Quality Sampling
- Determine if results from the general water
quality sampling program indicate a potentially
adverse water quality condition. - If appropriate, develop an additional sampling
program to further investigate the cause or
source of the potentially adverse water quality
condition. - Additional BMI Sampling
- Implement SWAMP to quantify BMI species
compositions, abundance, and distribution at
locations where potentially adverse water quality
issues may exist or are identified by the water
quality sampling program. - Develop sampling to address potential water
quality issues in consultation with the Aquatic
TWG.
6Potential Contingency Studies
- Additional Fish Sampling
- Fish Tissue Methyl Mercury Levels
- If methyl mercury in fish tissue exceeds the
OEHHA guidelines of 0.08 ppm during the initial
sampling, the Aquatic TWG will be consulted
concerning the need for additional sampling. - If additional sampling is deemed appropriate, a
sampling protocol will be developed. - Water Total Mercury Concentrations
- Fish tissue sampling may be expanded in the event
water quality sampling identifies locations that
are of potential concern due to the presence of
levels of total Mercury that exceed the EPA
Freshwater Aquatic Life criteria as described in
40 CFR 131.
7Water Quality Results
- Rivers and Streams
- In-situ field measurements
- General water quality parameters
- Voluntary enhanced water quality sampling
- Coliform sampling
8Water Quality Monitoring Locations
9Voluntary Enhanced Water Quality Sampling
Below Hell Hole Reservoir
Below French Meadows Reservoir
10Leakage Weir Flows
Study Site Name Weir Number
FM-A Weir 5
FM-B Weir 4
FM-C Weir 3
Note 10 gal/min 0.02 cfs 20 gal/min 0.5
cfs 50 gal/min 0.1 cfs
11Leakage Weir Flows
Study Site Name Weir Number
FM-A Weir 5
FM-B Weir 4
FM-C Weir 3
Note 10 gal/min 0.02 cfs 20 gal/min 0.5
cfs 50 gal/min 0.1 cfs
12DO and Metal Concentrations in French Meadows
Leakage Channels and Middle Fork American River
Iron (Fe) Criteria Taste and Odor 0.3 mg/L
(Basin Plan) Freshwater Aquatic Life Protection
1 mg/L (NTR) Manganese (Mn) Criteria 50 ug/L
(Basin Plan) (Taste and Staining) Dissolved
Oxygen (DO) Criteria 7.0 mg/L for Cold waters
(Basin Plan)
13Fecal Coliform Sampling Locations
14River and Stream Coliform Sampling
- All fecal coliform results in spring and fall met
listed objectives, except - North Fork Long Canyon Creek (RM3.0) in fall
- Ralston Afterbay near the Ralston picnic area
- Exceeded objectives on one day during 30-day, 5
sample sampling
15River Dissolved Oxygen Concentrations
16Reservoir Water Quality Results
- In-situ field measurements
- General water quality parameters
17Hell Hole Reservoir Temperature Profiles
18Hell Hole Reservoir Dissolved Oxygen Profiles
19French Meadows Reservoir Temperature Profiles
20French Meadows Reservoir Dissolved Oxygen
Profiles
21Fish Tissue Collection and Analysis for Methyl
Mercury
- Sample Locations
- Hell Hole Reservoir
- French Meadows Reservoir
- Middle Fork Interbay
- Ralston Afterbay
- Middle Fork American River near Otter Creek
confluence
22Fish Tissue Analysis Results
23Average Mercury Concentrations (mg/Kg-fish) and
Number of Fish
Fish Species French Meadows Hell Hole MFAM at Otter Creek Middle Fork Interbay Ralston Afterbay
Brown Trout (No.) 0.28 (2) 0.90 (6) 0.08 (1) 0.03 (6) 0.09 (4)
Lake Trout (No.) 0.00 (1)
Rainbow Trout (No.) 0.10 (3) 0.05 (1) 0.05 (9) 0.05 (4) 0.04 (1)
Sac Pikeminnow (No.) 0.25 (4)
Individual fish analyses only Excludes fish below
the following legal and/or edible size limits
LT 350 mm SPM 250 mm Bold values indicate
screening value of 0.08 mg/Kg were exceeded (Cal
EPA 2005 Klasing and Brodbery 2006).
24Guidance Fish Tissue Levels
Draft Fish Consumption Guidelines (OEHHA 2006)
25Guidance Fish Tissue Levels
26Safe Eating Guidelines Example
Draft Fish Consumption Guidelines for the Lower
Feather River (OEHHA 2006)
27Individual Fish Tissue Analysis Results
Fish Species French Meadows Hell Hole MFAM at Otter Creek Middle Fork Interbay Ralston Afterbay Total
Brown Trout 2 (5 composite) 6 1 6 4 19
Lake Trout 0 3 0 0 0 3
Rainbow Trout 3 1 9 4 1 18
Sac Pikeminnow 0 0 0 0 5 5
Total 5 ( 5 Composite) 10 10 10 10 45
2 LT were lt 350 mm (legal and/or edible size
criteria) (265 270 mm) 1 SPM was lt 250 mm
(legal and/or edible size criteria) (239 mm)
28 29Fish Tissue Analysis Results
30River and Stream In-situ Field Measurement Results
- All measurements met listed objectives or were
within expected ranges, except - Dissolved oxygen at Duncan Creek Confluence
- Duncan Creek above Middle Fork American River
confluence in spring - Middle Fork American River above Duncan Creek
confluence in spring - Middle Fork American River below Duncan Creek
confluence in spring - These locations were not surveyed in the fall
due to unsafe field conditions accessing the
sampling locations.
31River and Stream General Water Quality Parameter
Results
- All general parameters and dissolved metals
analyzed and total mercury samples met listed
objectives or were within expected ranges,
except - Dissolved manganese
- Middle Fork American River below French Meadows
gaging station in fall
32Voluntary Enhanced Water Quality Sampling
- Hell Hole Dam
- All in-situ field measurements and general water
quality parameters met listed objectives - French Meadows Dam
- In-situ field measurements
- pH and dissolved oxygen did not meet water
quality objectives - General water quality parameters
- Iron and manganese concentrations exceeded water
quality objectives
33Reservoir In-situ Field Measurement Results
- All measurements met listed objectives or were
within expected ranges, except - Dissolved oxygen
- Hell Hole Reservoir in fall
- French Meadows Reservoir in spring and fall
- Two locations in spring
- One location in fall
34Reservoir General Water Quality Parameter and
Fecal Coliform Results
- All general parameters and dissolved metals
analyzed and total mercury samples met listed
objectives or were within expected ranges. - All fecal coliform results in spring and fall met
listed objectives.
35Fish Tissue Analysis Results
- Methyl mercury concentrations in at least 1 fish
from each location exceeded the OEHHA screening
value (0.08 mg/kg fish). - 23 of 45 individual fish analyzed exceeded the
screening value. - Highest concentrations were measured in fish from
Hell Hole Reservoir, where largest fish were
caught.