references - indexTHE WES HANDBOOK ON WATER QUALITY ENHANCEMENT TECHNIQUES FOR RESERVOIRS AND TAILWATERS REFERENCES APPENDIX 2.1A Simple Random SamplingAPPENDIX 2.1.A. SIMPLE RANDOM SAMPLINGSTRATIFIED RANDOM SAMPLINGThree steps to stratified samplingStratified Sampling ExampleStratified Sampling Example (COnt.)Assume a sample size of 52 was calculatedEqual Allocation Proportional Allocation Optimal AllocationSYSTEMATIC SAMPLINGApparent advantages over simple random samplingAPPENDIX 2.1 B: Sampling Design Software User's Manual.. by. Robert F . Gaugush Sampling Design Software User's Manual - references0016Notice to Program RecipientsSampling Design Software User's Manual - references0018Waterways Experiment Station Cataloging-in-Publication Data - references0019Contents - references0020Contents (cont.) - references0021Introduction - references0024Contents of the SDS Diskinstallation - references0026Hardware RequirementsDecision Matrices - references0028Data EntryError MessagesDocumented SessionDecision Matrices - references0032Decision Matrices (Cont.)Matrix Out DECISION MATRIXDECISION MATRIX (Cont.)Sample SIZE - references0037Cost SAMPLE SIZE - references0039Example Output FileVariance Component Analysis An Example Data Set EG,VAR, is Provided on the SDS Distirbution Diskette and is Shown Below An Example Data Set EG,VAR, is Provided on the SDS Distirbution Diskette and is Shown Below (Cont.) - references0043An Example Data Set EG,VAR, is Provided on the SDS Distirbution Diskette and is Shown Below (Cont.) - references0044Program Execution - references0045Error Messages Select output route - references0047Select output route - references0048Disk fiel name for output eg.out Variance Component Analysis Variance Component Analysis (Cont.)Example Output File - references0052Error Analysis - references0053Program Execution - references0054Error Meassages Error Analysis Sampling Design Software- Version 2.0 Select output route - references0057Select output route (Cont.)Input data file name? eg.err Stratified Smaple Statistics Strata statistics Error Analysis - references0062Error Analysis (cont.) - references0063Error Analysis (cont.) - references0064repaet program with new data ( Y or N )Example Output File - references0066Cluster Analysis - references0067Data Set Preparation Program Execution - references0069Documented Session Cluster Analyssi Smapling Design Software - Version 2.0 Output data file name? eg.out Clustering Method Clustering Method (cont.) - references0074Clustering Method (cont.) - references0075Cluster Analysis - references0076Cluster Analysis (cont.)Geometric Scale Short descriptions of various portions of the output are available This section of the output provides a tabular display of the data used to develop the dendrogram The graphical display form a cluster analysis is referred to as a clendrogram because of its tree - like apperance Example Output File - references0082Example Output File (Cont.)References - references0084Bibliography Bibliography (cont.)Report Documetation Page Appendix 2.2A The NONPOINT SOURCE MANAGER'S GUIDE TO WATER QUALITY AND LAND TREATMENT MONITORINGThe Nonpoint Source Managers Guide to Water Quality and Land Treatment Monitoring The Nonpoint Source Manager's Guide to Water Quality and Land Treatment Monitoring Acknowledgements - references0091Important MessagesOverview of Monitoring ProgramIntroduction - references0097Figure 1.1 The development of a nonpoint source control monitoring program.Overview of a Monitoring ProgramFigure 1.2 Land treatment and water quality monitoring program design Management Objectives and Problem Documentation Monitoring Program ObjectivesTable 3.1 Monitoring Objectives and Level of DetailVariable SelectionTable 3.2. Example Primary Variables and Explanatory Variables for Trend Monitoring.Monitoring to Detect Ecosystem ImpactsLevel Land Treatment and Land Use MonitoringTable 3.3 Land Use and Land Treatment Explanatory VariablesStream Monitoring LocationsWater Quality Monitoring VariablesColiform BacteriaMacrophytesZooplanktonHabitat VariablesLake Fish HabitatTemperatureTransparencyPhyfoplanktonPeriphytonMacrophytes Stream Macroinvertebrate HabitatStream Fish HabitatTransects, Maps, and Aerial Photography for Habitat Measurements.Figure 3.2a Transects for habita evaluation perpendicular to the main direction of stream flow.Figure 3.3a b Stream section diagrams to illustrate detailed mapping analyses of fish habitat.Energy and organic matter processing in the stream ecosystem. Riparian and Shoreline Habitat Evaluations Chemical and Physical MonitoringSedimentation.Level II Pollutant Loading Rate Monitoring Monitoring Program DesignFormulating a Specific Monitoring ObjectiveProblem DocumentationProblem Documentation Sample TimingDetecting TrendsDetecting ImpactMinimum Detectable Change Experimental DesignsFigure 4.2. Upstream/down- stream and pre- and post - BMP desgin Multiple Watersheds and Pre- and PostSubwatershedLakes and ReservoirsFigure 4.4 Total number of ampling events vs magnitude of linear trend. (after al. 1989) Preliminary SamplingCoverage Through TimeMonitoring Explanatory Variables Data CollectionData Analysis - references0152Program EvaluationConclusions - references0156References - references0158References (Cont.) - references0159References (Cont.) - references0160References (Cont.) - references0161References (Cont.) - references0162References (Cont.) - references0163References (Cont.) - references0164Glossary Glossary (Cont.) - references0167Glossary (Cont.) - references0168Glossary (Cont.) - references0169EPA Evaluation of the Experimental Rural Clean Water Program EVALUATION of the EXPERIMENTAL Rural Clean Water Program Water Qualify Evaluation, and Monitoring Reporting Water Qualify Evaluation, and Monitoring Reporting (cont.) - references0173Water Qualify Evaluation, and Monitoring Reporting (cont.) - references0174Water Qualify Evaluation, and Monitoring Reporting (cont.) - references0175Water Qualify Evaluation, and Monitoring Reporting (cont.) - references0176Water Qualify Evaluation, and Monitoring Reporting (cont.) - references0177Water Qualify Evaluation, and Monitoring Reporting (cont.) - references0178Water Qualify Evaluation, and Monitoring Reporting (cont.) - references0179Water Qualify Evaluation, and Monitoring Reporting (cont.) - references0180Appendix 2.4A Evaluation of Methods for In Situ Monitoring of Releases from Hydro power Projects by Michael C. Vorwerk, William E. Jabour, and Joe H. Carroll Purpose - references0182Manual Sampling Successful Example Figure 1. manual sampling locations for Chattahoochee River below West Point Dam Automated Remote Monitoring Representativeness of a Sample Location Figure 2. Plan view of dam monitoring locations In-Lake Automated Profiles Tapping Water from Spiral Case Downstream Face of Dam Sonde Delopyed in Protective Pipe in Tailwaters InterferenceReferences Appendix 2.4B. Remote Monitoring of Hydroprojects: Design, Installation, and Verification of Remote Monitoring Systems by: John W. Lemons, Michael C. Vorwerk, Joe H. Carroll, and William E. JabourPurpose - references0196Figure 1. Flow diagram for water quality automated monitor system designSite CharacterizationIce Harbor ExampleMonitor EquipmentSoftwareFigure 4. Savannah River basinFigure 6. Hartwell Dam operation and release temperaturesFigure 8. Richard B. Russell piping gallery monitorBull Shoals DamConclusions - references0206Point of Contact - references0207Appendix 2.4C . Statistical Verification of Mean-Value Fixed Water Quality Monitor Sites in Flowing Waters by: Michael Vorwerk, Joe Carroll, and John LemonsPurpose - references0209Figure 1. Possible sources of heterogeneities in flowing waterApproach for Mean DataStatistical ComparisonDetermining the Power of the Test - references0213Example 1: Columbia River Camas/Washougal Station--Hand CalculationTable 2. Differences (D), Squares of Differences (D2), and Totals for Data Specified in Table 1 (Sample Size, n = 8)Figure 6. Normal probability plot of the differences between transect and fixed monitor station pairs of observations.Example 2: Columbia and Snake Rivers Fixed Monitoring SystemTable 3. Verification of Fixed Monitor Station Location with Transect DataDetermining the Power of the Test - references0219Table 4. Calculation of Parameters Needed to Determine d, β, and the Power of the TestConclusions - references0221Point of Contact - references0222Appendix 3.1A . Elements of a Model Program for Nonpoint Source Pollution Control by: Steven W . Coffey, Jean Spooner Daniel E. Line, Judith A. Gale, Jon A. Arnold, Deanna L. Osmond, and Frank J. HumenikElements of a Model Program for Nonpoint Source Pollution Control Results - references0226Program Administration and ManagementProgram Technical S u p p o r tProject SelectionProgram FundingProject Proposal and Plan of Work DevelopmentProject Technical SupportImplementing the Plan of WorkImplementing the Plan of Work (Cont.) - references0234Implementing the Plan of Work (Cont.) - references0235Feedback LoopConclusionReferences - references0238Appendix 3.1B Planning and Managing a Successful Nonpoint Source Pollution Control Project by: Judith A. Gale, Deanna L. Osmond, Daniel E. Line, Jean Spooner, Jon A. Arnold, Gregory D. Jennings, and Frank J. HumenikPlanning and Managing a Successful Nonpoint Source Pollution Control ProjectDocument the Water Quality ProblemDefine Objectives and GoalsObtain FundingDefine the Critical AreaAssessing Project Effectiveness]References - references0246North Carolina Cooperative Extension Service - references0247Appendix 4.1 C Farmer Participation in Solving the Farmer Participation in Solving the Nonpoint Source Pollution Problem by: Deanna L. Osmond and Judith A. GaleFarmer Participation in Solving the Nonpoint Source Pollution ProblemIncentives To Producer ParticipationTechnology Transfer: The Importance of Information and Education Programs Environmental ConcernsKey Points of Farmer ParticipationThe Importance of Information and Education ProgramsReferenceNorth Carolina Cooperative Extension Service - references0256Appedix 4.2 A . BEST MANAGEMENT PRACTICES DEFINITIONS AND DESCRIPTIONSAppendixConservation Cover (327)Contour Farming (330)Contour Stripcropping (585)Crop Residue Use (344):Diversion (362)Filter Strip (393)Grassed Waterway (412)Hedgerow Planting (422):Irrigation System, Drip or Trickle (441)Irrigation Water Management (449):Lined Waterway or Outlet (468):Mulching (484)Precision Land Forming (462)Pumped Well Drain (532)Spring Development (574)Surface Drainage Field Ditch (607)Waste Management System (312)Water and Sediment Control Basin (638):Wetland Restoration (657A)Appedix 4.2B EXAMPLES OF COSTS FOR BMPsNORTH CAROLINA AGRICULTURE COST SHARE PROGRAM AVERAGE COST FOR PROGRAM YEARS 1997-1999 NRCS AREATABLE 1NRCS AREA 3 AVERAGE COSTS for AGRICULTURE COST S&E Program years 1997-1999 AVERAGE COST LIST FOR BMP COMPONENTSFilter StripDiversionTerraceSpring Development (from water source to junction box - maximum of 2 spring developments per trough/tank charged to NCACSP )Stream Crossings and Stock TrailsStream Crossings and Stock Trails (Cont.)Components of Waste Management Structures/SystemsDry Stack/Litter Storage Facility with roof (Maximum size cost-shared is based on storage required in waste utilization plan, average stacking height of 5 feet.)Dry Stack/Litter Storage Facility with roof (Maximum size cost-shared is based on storage required in waste utilization plan, average stacking height of 5 feet.) (Cont.)Slurry Storage StructureControlled Livestock Lounging AreaGrade Stabilization StructuresSediment BasinWater Control Structures - references0298Roofed Agri-Chemical Handling Facility Roofed Agri-Chemical Handling Facility (Cont.)Riparian Buffer Streambank Stabilization COMPONENTS WHICH ARE COMMON TO TWO OR MORE PRACTICESGrading and shapingConcrete and MasonryPipe and fittings ( all prices includes installation ) Pipe and fittings ( all prices includes installation ) (Cont.)Pipe and fittings ( all prices includes installation ) (Cont.) - references0308Pipe and fittings ( all prices includes installation ) (Cont.) - references0309Pipe and fittings ( all prices includes installation ) (Cont.) - references0310Pipe and fittings ( all prices includes installation ) (Cont.) - references0311Pipe drops and surface inlets (installed)Appendix 4.2C. COST EFFECTIVENESS STUDYCost-Effectiveness of Agricultural BMPs for Nutrient Reduction in the Tar-Pamlico Basin - references0314Cost-Effectiveness of Agricultural BMPs for Nutrient Reduction in the Tar-Pamlico Basin - references0315Executive Summary - references0316Results - references0317Results (Cont.)Table ES-1 Summary of Nutrient Reduction Cost-Effectiveness Estimates for Cost-Shared Practices in the Tar-Pamlico Basin'Table ES-1 ( Continued ) - references0320Table ES-1 ( Continued ) - references0321Chapter 1 Definition of TermsChapter 2. Developing BMP Cost Effectiveness Values for the Tar-Pamlico BasinSources of BMP Effectiveness DataFigure 2-1. Chesapeake modeling subbasins in ecoregions common to the Tar-Pamlico Basin.Cost-Effectiveness Calculation MethodsEquations for Calculating.Cost-EffectivenessResults - references0337Animal Waste ManagementLand ApplicationEffectiveness of Land Application Relative to Typical Preexisting Conditions Table 2-3. Surface and Subsurface Losses from Land Application of Animal WastesEffectiveness of Land Application Relative to Typical Preexisting Conditions (Cont.)Table 2-4. Estimates of Surface and Subsurface Nutrient Loss from Land ApplicationTable 2-5. Cost-Effectiveness of Agronomic Land Application Relative to Excess ApplicationTable 2-6. Effectiveness of Land Application Relative to Direct DischargeTable 2-7. Cost-Effectiveness of Land Application Relative to Direct DischargeLagoon Effectiveness Relative to Typical Preexisting ConditionsLagoon Effectiveness Relative to Typical Preexisting Conditions (Cont.)Lagoon Effectiveness Relative to Direct DischargeTable 2-10. Cost-Effectiveness of Anaerobic Lagoons Relative to Land Application at Excess Rates Lagoon Effectiveness Relative to Direct Discharge (Cont.)Table 2-11. Effectiveness of Lagoon Cost-Sharing Relative to Direct Discharge'Table 2-12. Cost-Effectiveness of Anaerobic Lagoons Relative to Direct DischargeComposting of Poultry MortalityWater Control Structures - references0355Table 2-13. Water Control Structures Cost DataTable 2-14. Effectiveness and Cost-Effectiveness of Water Control StructuresTable 2-15. Cost Data for Grassed Waterways and DiversionsTable 2-16. Cost Data for Croplan ConversionTable 2-17. Cost Data for Conservation Tillage Figure 2-2. Conservation tillage effectiveness Table 2-18. Cost Data for TerracingTable 2-19. Effectiveness Estimates for TerracingTable 2-20. Cost Data for VFSs, Field Borders, and StripcroppingTable 2-21. Effectiveness data for VFSs, Field Borders, and StripcroppingFigure 2-5. Vegetated filter strip cost-effectiveness.Nutrient ManagementFigure 2-6. Nutrient management cost-effectiveness.Table 2-22. Summary of Nutrient Reduction Cost-Effectiveness Estimates for Cost-Shared Practices in the Tar-Pamlico Basin'Table 2-22 (continued) - references0370Table 2-22 (continued) - references0371Figure 2-7. Summary of nutrient removal cost-effectiveness rangesChapter 3: The Need for a Safety Factor Site-Specific VariabilityMaskingSimulated Field Conditions/Sampling TechniquesCost EscalationChapter 4. Discussion and Recommendations The Agricultural Cost-Share Program could place a higher-priority on nutrient (and particularly, nitrogen) managementincreasing the cost-effectiveness of cost-sharing will require an increased commitment to education and technical assistanceThe lack of information specific to nonpoint source nutrient management activities in the basin is a handicap to studies of this typeReferences - references0384References (cont.) - references0385References (cont.) - references0386References (cont.) - references0387References (cont.) - references0388Appendix 1: The Tar-Pamlico Nutrient Trading Program Determining initial Load Reduction, Goals, and CostsImplementing the Nutrient Trading ProgramTable A1-1. Schedule of Nutrient Loads and PaymentsFunding BMP implementation and Maintenance Appendix 2. The Chesapeake Bay Watershed ModelApplication HistoryAppendix 3. Summary of BMP Cost Data for Counties in the Tar-Pamlico BasinConventional Tillage Cropland Loading Factors for Chesapeake Subbasins in Ecoregions 63 and 65 (Carnacho, 1992)Appendix 5. Calculation of Trading Values for Phase and Phase IIEstimation of BMP Nutrient Load ReductionsEstimating a trading valuePhase II Trading ValueAppendix 6: Calculations of Effectiveness and Cost-Effectiveness for Animal Waste PracticesAppendix 6: Calculations of Effectiveness and Cost-Effectiveness for Animal Waste Practices (Cont.)Calculation of Land Application Cost Effectiveness Relative to Direct Discharge Calculation of Lagoon Cost-effectiveness realtive to Excess and ApplicationAnaerobic Lagoon Cost Conversions Appendix 4.9A. WATER QUALITY MANAGEMENT FOR RESERVOIRS AND TAILWATERS by: G. Dennis Cooke and Robert H. KennedyPart III: PRERESERVOIR TREATMENTTheory and Design - references0413Prereservoir phosphorus removal - references0414Wetlands - references0415Diversionary streamsPrereservoir phosphorus removal - references0417Wetlands - references0418Limitations and Concerns - references0419Siltation basins and wetlandsSummary - references0421Table 2. Summary of Prereservoir TreatmentsReferences - references0423References (Cont.) - references0424References (Cont.) - references0425Part IV. HOSPHORUS INACTIVATIONTheory and Design - references0427Theory and Design (cont.) - references0428Figure 6. Changes in dissolved aluminum concentration (dashed line) and total alkalinity (solid line) for water from Ohio Figure 7. Estimated aluminum sulfate dose (mg Al required to obtain pH6 (i.e., "maximum dose")Theory and Design (Cont.) - references0431Figure 8. Generalized diagram of an alum application system (from Kennedy and Cooke 198'2)Effectiveness, Costs, and Feasibility - references0433Annabessacook Lake, Maine.Lake Charles East, Indiana.Limitations and Concerns - references0436Limitations and Concerns (cont.) - references0437Summary - references0438Table 3. Summary of Phosphorus InactivationReferences - references0440References (Cont.) - references0441References (Cont.) - references0442Part V: DILUTION AND FLUSHINGTheory and Design Theory and Design (Cont.)Figure 9. Percent change in in-lake phosphorus concentration following dilution with water containing no phosphorusFigure 10. Percent change in in-lake phosphorus concentration following dilution with water having a phosphorusEffectiveness, Costs, and Feasibility - references0448Green Lake, WashingtonLimitations and Concerns - references0450Table 4. Summary of Dilution and FlushingReferences - references0452Part VI: SEDIMENT REMOVALApplication of the methodsediments and sediment budgetDredge selectionDetermination of sediment removal depthEffectiveness and CostsLimitations and Concerns - references0459Limitations and Concerns (Cont.) - references0460Summary - references0461References - references0462References (Cont.) - references0463References (Cont.) - references0464References (Cont.) - references0465Part IX: WATER LEVEL Drawdown Theory and Design - references0468Table 10. A Summary of the Response of Some Common Nuisance Macrophytes to Drawdown (Modified from Cooke et.al 1986) Effectiveness, Costs, and Feasibility - references0471Limitations and Concerns - references0472Summary - references0473Table 11. Summary of Water Level Drawdown References - references0475Part X: HARVESTINGEffectiveness, Costs, and Feasibility - references0477Effectiveness, Costs, and Feasibility (Cont.) - references0478Effectiveness, Costs, and Feasibility (Cont.) - references0479Effectiveness, Costs, and Feasibility (Cont.) - references0480Table 12. Comparison Between Midwest and Florida Cost Ranges (1987 Dollars) for Harvesting and Herbicide Treatments of Lakes and ReservoirsLimitations and Concerns - references0482Summary - references0483Table 13. Summary of HarvestingReferences - references0485References (Cont.) - references0486Part XI: BIOLOGICAL CONTROLSReproductionFood preferencesTable 14. Feeding Preference List, in Approximate Order of Preference, for Triploid Grass Carp in Florida, Illinois, and Oregon-Washington StudiesTable 14. (Continued)Table 14 (Concluded) - references0493Food preferences (Cont.)Stocking ratesCase historiesEnvironmental Impacts - references0497Environmental Impacts (Cont.)Insects and Plant PathogensInsects and Plant Pathogens (Cont.) - references0500Insects and Plant Pathogens (Cont.) - references0501BiomanipulationFigure 14. The aquatic food chain, indicating between the components of the biomanipulation modelBiomanipulation (cont.) - references0504Biomanipulation (cont.) - references0505Biomanipulation (cont.) - references0506Summary - references0507References - references0508References (Cont.) - references0509References (Cont.) - references0510References (Cont.) - references0511References (Cont.) - references0512References (Cont.) - references0513PART XII: Sediment Covers Theory and Design - references0515Effectiveness, Costs, and Feasibility - references0516DartekPolypropyleneOther materialsLimitations and Concerns - references0520Table 16. Summary of Features of Sediment Covering MaterialsTable 17. A Summary of Sediment CoversReferences - references0523Part XIII: HERBICIDES AND ALGICIDESEffectiveness and FeasibilityCopper-containing compoundsEndothallEndothall (Cont.)FluridoneTable 18. Common Aquatic Weed Sepcies and Their Responses to Herbicides Table 18 (Concluded)Costs Limitations and Concerns - references0533Summary - references0534Table 19. Summary of Algicides and HerbicidesReferences - references0536References (cont.) - references0537References (cont.) - references0538References (cont.) - references0539References (cont.) - references0540References (cont.) - references0541handbook on Water Quality Enchacement techniques for Reservoirs and Tailwaters