Rapidan river watershed assessment presentation john ndiritu 2014
Transcript of Rapidan river watershed assessment presentation john ndiritu 2014
RAPIDAN RIVER WATERSHED ASSESSMENT
SUMMARY
Rapidan river is the largest tributary
of the 195 mile Rappahannock River
Drains the eastern portion of the
Blue Ridge Mountains, Shenandoah
National Park to the Chesapeake
bay.
EPA classification as “impaired”
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SUMMARY
Agricultural practices, human
development (residential, commercial,
infrastructural) and climate change has
affected the quality and quantity of the
river water over the years
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WATER ISSUES
UTILITY ABSTRACTION AND DISCHARGE
TOWN OF GORDONSVILLE
ORANGE TOWN
LOCUST GROVE
VA withdrawals, 2012
RAPIDAN RIVER WATERSHED ASSESSMENT
WATER ISSUES
Water Quality in privately owned wells, springs and cisterns
Presence of:
Total coliform bacteria
Sodium
manganese
Low PH (Acidic)
SOURCE OF DATA: VIRGINIA COOPERATIVE EXTENSION, 2010. WWW.EXT.VT.EDU
RAPIDAN RIVER WATERSHED ASSESSMENT
WATER ISSUES
OTHER NON POINT SOURCES OF POLLUTION
Table from VDEQ,2007
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DISCHARGE POINT SOURCES ALLOWED UNDER VPDES (PERMITS REQUIRED)
RAPIDAN SERVICE AUTHORITY
TOWN OF GORDONSVILLE
OTHERSFigure from VDEQ, 2007
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CURRENT DISCHARGE AND WATER QUALITY NETWORK
ORGANIZATIONS NATIONAL WEATHER SERVICE-
STREAM GAUGES
VIRGINIA DEPARTMENT OF EMERGENCY MANAGEMENT-STREAM AND RAIN GAUGES, INFLOWS
VIRGINIA DEPARTMENT OF ENVIRONMENTAL QUALITY (EPA SHARING)-WATER QUALITY SAMPLING
UNITED STATES GEOLOGICAL SURVEYS-STREAM
PRIVATE AND NON PROFIT DATA COLLECTION
MAP FROM HTTP://WWW.NAO.USACE.ARMY.MIL/PORTALS/31/DOCS/
RAPIDAN RIVER WATERSHED ASSESSMENT
RAPIDAN FLOOD RISKCAUSE OF BANK EROSION AND LANDSCAPE DEGRADATION-TURBIDITY AND SEDIMENTATION
• HURRICANE AGNES JUNE 1972. PRECIPITATION WAS 6 INCHES A DAY. JAMES RIVER VIRGINIA CRESTED 36.5 FEET, HIGHEST IN 200 YEAR (VDEM, 2014). DAMAGE: 1400 HOMES; ROADS, BRIDGES DESTROYED; 13 PEOPLE KILLED; COST OF DAMAGE AMOUNTED TO $325 MILLION.
• DEVASTATING FLOODING OF 1977 AFFECTED KENTUCKY, VIRGINIA AND WEST VIRGINIA. NATIONAL WEATHER SERVICE (NWS) INITIATED NATIONAL FLASH FLOOD DEVELOPMENT IN 1978, INFLOWS DEVELOPED FROM THIS AS JOINT EFFORT WITH STATES.
• PROTOTYPE STARTED 1980, 12 COUNTIES ON THE APPALACHIAN, SUSCEPTIBILITY TO FLOODING (VDEM, 2014).
• 1985, CONGRESS APPROVED NWS INFLOWS FUNDING;
EXPAND TO COVER BEYOND INITIAL 7 STATES. LINKED AND INTEGRATED DATA AND INFORMATION THROUGH 250 COMPUTERS; 1500 SENSORS; 12 STATES AND 120 COUNTIES.
Rapidan River bank erosion at Route 3
RAPIDAN RIVER WATERSHED ASSESSMENT
Virginia Department of Conservation and Recreation
2010 NonPoint Source (NPS) Assessment Prioritization Data Query Results-Rapidan River Watershed, HU RA37
NPS Impaired Waters Rankings Based on Percentage of Existing Waters by Type
Rank Definitions: A - Very High Percentage Impaired B - High Percentage Impaired C - Moderate Percentage Impaired (Rapidan River Watershed) D - Low Percentage Impaired E - No Impairments blank - No Rivers or Lakes/Reservoirs
Export to Comma Delimited File
Virginia Hydrologic
Unit
Miles of Impaired
Rivers
Acres of Impaired
Lakes
% of River Miles
Impaired
% of Lake Acres
Impaired
IMP River Rank
IMP Lake Rank
RA37 7.91 0.00 24.19 0.00 C E
Rapidan River http://dswcapps.dcr.virginia.gov/htdocs/progs/npsimpbio10_results.aspx
Historic floods Recent floods
(1) 30.40 ft on 06/28/1995(2) 30.30 ft on 10/16/1942(3) 29.53 ft on 06/22/1972(4) 28.03 ft on 04/26/1937(5) 27.49 ft on 09/07/1996
(1) 17.16 ft on 05/17/2014(2) 14.75 ft on 05/01/2014(3) 16.51 ft on 06/10/2013(4) 14.35 ft on 05/08/2013(5) 13.49 ft on 01/31/2013
NOAA: http://water.weather.gov/ahps2/hydrograph.php?wfo=lwx&gage=clpv2
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Snapshot sampling of watershedProtocol 9: Aquatic chemistry
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Rapidan River Watershed assessment
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Test Factor Data Result Rank Condition
Dissolved Oxygen 4ppm at 6o C <50% saturation (31%) 1 Poor
BOD 8ppm 4ppm 3 Good
Coliform Bacteria Positive Positive 1 Poor
pH 8 8 3 Good
Temperature 60 C N/A N/A N/A
Nitrate 5ppm 5ppm 2 Fair
Phosphate 1ppm 1ppm 4 Excellent
Turbidity 40JTU 40JTU 3 Good
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Discussions
The state of the watershed is determined by the human and natural disturbances in space and time. Rapidan River Watershed (RRW) has had history floods particularly during storms and hurricanes. The most immediate danger to human life, infrastructure, aquatic life and the ecosystems is therefore FLOODING.
More real-time stream and rainfall gauges would help mitigate the imminent danger to human life. The Army Corp of Engineers has plans (2015) to install 7 real-time gauges to add to the 8 already in existence in the Upper and Middle Rapahhanock River.
Water quality gauges will be added in RRW in following stream: Marsh Run, Blue Run, Rapidan River (2), Unnamed tributary, and Cedar Run.
Non point pollution could be associated with the intensive agricultural activities in RRW, human settlement, natural disturbances and climate change. In some parts of the Rapidan River, the riparian buffer is thin or lacking. Livestock foraging is extensive within the flood zones.
Point source pollution could originate from permitted private or utility water suppliers or consumers particularly in irrigation agriculture (horticultural production).
Privately owned water supplies (wells, cisterns, spring) have unique water quality issues mainly related to the geology and sanitation. Awareness creation is being conducted Virginia Cooperative Extension of VT.
Shady areas, enough sun, clear water, fast riffle, adequate dissolved oxygen, and clean stream bed would be supportive of aquatic life. Good BOD from snapshot sampling supports this assertion as the data from VDEQ sampling.
Nutrient concern is still an issue in the RRW as indicated by the EPA TMDL Implementation Plan and the sampling in the lower RRW done by the author.
Watershed Organizations such as Friends of the Rappahannock have programs to address issues of litter removal and recycling, storm drain labeling initiative, roof water harvesting, community clean-ups installation of green infrastructure and more.
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CONCLUSIONS
The snapshot water quality measurements indicated that the Rapidan River had adequate dissolved oxygen to support aquatic life. Water odors and surface oils were generally lacking. Sediments deposits was characterized as silt or suspended sediments. This would reduce in base flow period. Substrate size was generally supportive of invertebrates with substantial proportions of riffle substrate consisting of boulder, cobble, and gravel.
Mix of sunny areas and shade stretches is also supportive of many invertebrate species. Nitrate concentration could be from agricultural activities prevalent in RRW. This sampling was done
during low agricultural activity season (Late Fall). Higher levels of nutrient might could be expected during active seasons.
From documented data and information and the snapshot sampling done, the author contends that the
state of the RRW is FAIR. EPA considers it “Impaired” under the TMDL WIP.
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Reference
EPA, 2014. Watershed assessment, tracking and environmental results. Web-based EPA data o water quality. http://ofmpub.epa.gov/tmdl_waters10/attains_waterbody.control?p_au_id=VAN-E13R_RAP02A06&p_state=VA&p_cycle=2006
USACE, 2013. Middle and Upper Rappahannock River Basin, Virginia. Rainfall, Stream and Water Quality Gauging Analysis. http://www.nao.usace.army.mil/Portals/31/docs/business/FPMS/PASDocuments/App_A_4a.pdf
Virginia Cooperative Extension, 2010. Evaluation of household water quality in Madison and Orange Counties, Virginia. www.ext.vt.edu
Virginia Water Quality Assessment 305(b) Report, 2010 Nonpoint source Assessment, Prioritization and Activities.http://www.deq.virginia.gov/Portals/0/DEQ/Water/StormwaterManagement/NPSChapt4.1.pdf
VDEQ, 2013. Status of Virginia’s water resources. A report on Virginia’s water resources management activities. www.vdeq.gov
VDEQ, 2007. Upper Rappahannock River Basin bacteria TMDL development. Technical Advisory Committees. http://www.rrregion.org/pdf/TMDLs/2008/Rappahannock_TAC_Mtg1_ECI.pdf