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Water Quality in Lakes & Streams Dr. Philip Bedient Introduction Water quality management is the science that predicts how much waste is too much for a body of water Assimilated- amount of waste that can be tolerated by a body of water Determined by knowing the type of pollutants discharged and their effect on water quality Water Quality Management Water quality is affected by natural factors: Historical uses in the watershed Geometry of the watershed area Climate of the region Good water quality protects drinking water as well as wildlife Point Sources of Pollutants Point sources include domestic sewage and industrial wastes Point sources - collected by a network of pipes or channels and conveyed to a single point of discharge in receiving water Municipal sewage - domestic sewage and industrial wastes that are discharged into sanitary sewers - hopefully treated Point source pollution can be controlled by waste minimization and proper wastewater treatment Nonpoint Sources Urban and agricultural runoff that are characterized by overland discharge This type of pollution occurs during rainstorms and spring snowmelt Pollution can be reduced by changing land use practices Combined Sewer Flow Nonpoint pollution from urban storm water collects in combined sewers Combined sewers- carry both storm water and municipal sewage - older cities Combined Sewer Overflow Eliminating this involves: Construction of separate storm and sanitary sewers Creation of storm water retention basins Expanded treatment facilities to treat the storm water Combined sewers are not prohibited by the U.S. because removal would disrupt streets, utilities, and commercial activities Oxygen- Demanding MATERIAL Dissolved Oxygen (DO)- fish and other higher forms of aquatic life that must have oxygen to live Oxygen- Demanding Material- anything that can be oxidized in the receiving water resulting in the consumption of dissolved molecular oxygen - BOD, COD Almost all naturally occurring organic matter contributes to the depletion of DO Nutrients Nitrogen and phosphorus are considered pollutants when too much present in high conc. High levels of nutrients cause disturbances in the food web Organisms grow rapidly at the expense of others Major sources of nutrients (N, P): Phosphorus-based detergent Fertilizer and agricultural runoff Food-processing wastes Animal and human waste Pathogenic Organisms Include bacteria, viruses, and protozoa from diseased persons or animals Water is made unsafe for drinking, swimming, and fishing Antibiotic-resistant bacteria are the most dangerous Bacteria are found in both urban and rural environments with no observable pattern Pathogenic Organisms Serious Outbreaks of these cause great suffering E. Coli - indicator of fecal coliform bacteria Salmonella (typhoid fever) Shigella (dysentery) Cryptosporidium - protozoa Giardia- protozoa Suspended Solids Suspended solids- organic and inorganic particles that are carried by wastewater into a receiving water A slower flow causes particles to settle and form sediment Colloidal particles- do not settle, cause an increase in the turbidity of surface water Organic suspended solids- exert oxygen demand Inorganic suspended solids- result from soil erosion Suspended Solids With an increase in the amount of sediment comes: Increase of turbidity Decrease of light penetration Increase in amount of bacteria Increase in solids settled on the bottom which causes animal habitats to be destroyed Salts Total dissolved solids - TDS Water collects salt as it passes over soil during irrigation practice Too much salt can cause crop damage and soil poisoning Arid regions - west and south Texas Toxic metals and toxic organic compounds Agricultural runoff contains pesticides and herbicides Urban runoff contains zinc - from tires Too many toxic metals and toxic organic substances can leave a body of water useless James River in Virginia Passaic River in New Jersey Toxic compounds can also make fish and shellfish unsafe to eat - As, Hg, Pb, and PCBs The new concern is pharmaceutical chemicals in water and wastewater Endocrine-Disrupting Chemicals (EDCs) These include Polychlorinated biphenyls Pesticides Phthalates No suitable method exists to characterize EDC’s Can mimic estrogens, androgens, or thyroid hormones Interfere with regular animal reproduction Affects synthesis of hormones in the body Arsenic A naturally occurring element - As2O3 of real concern. Caused by minerals dissolving naturally from weathered rocks and soils - iron oxides and sulfides Causes many health effects such as: Arsenic poisoning - interfere with ATP cycle Circulatory disorders Gastrointestinal upsets Diabetes Skin lesions & possible skin cancers Created a huge problem in Bangladesh wells in 1992 Arsenic - October, 2001 EPA lowered the MCL from 50 to 10 ug/L Mostly a problem in western U.S. and the Midwest - naturally occurring Lifetime excess risk translates to 30/10,000 Compares to other carcinogens - 1/105 to 1/106 Major concern in water supplies now Heat Impacts An increase in the Temp of water can cause: Increase in DO which leads to a deterioration in water quality Large fish kills Blocked migration of fish Altered genetic makeup in fish Taste and Odor Problems An increase in MTBE concentration in water Releases from USTs and watercraft engines Has impacted many lakes nationwide Created serious taste and odor problems City of Dallas shut down main water supply intakes due to largest pipeline spill in the U.S. in 2000 City of Santa Monica closed main wells - 1999 Many private wells impacted by MTBE Water quality management in rivers Main goal is to control the discharge of pollutants so that water quality is not degraded above the natural background level Controlling waste involves: 1) Measuring pollutants levels (x,z, t) 2) Predicting their effect on the water quality 3) Determining background water quality that would be present without human intervention 4) Evaluate the levels acceptable for intended uses of the water River Pollution Impacts Waste Input Receptor Simple Mass Balance Input rate - Output rate - decay rate = Accumulation rate Steady state conservative system Stream Qs, Cs C = Qw Cw + Qs Cs Qs + Qw Waste Input Qw, Cw Simple Mass Balance Input rate - Output rate - decay rate = Accumulation rate Steady state conservative system Qs = 10 m3/s 26.67 mg/L Cs = 20 mg/L C = 20 (10) + 40 (5) (10 + 5) Waste Input Qw = 5 m3/s Cw = 40 mg/L Transport characteristics that affect concentration • Velocity • Dilution (mixing) v • Dispersion • Degradation (mass loss) • Adsorption (to soils) • Sedimentation (to bottom) • Aquatic Life (attached) Effect of Oxygen-demanding wastes on rivers Depletes the dissolved oxygen in water Threatens aquatic life that require DO Concentration of DO in a river is determined by the rates of photosynthesis of aquatic plants and the rate of oxygen consumed by organisms Biochemical oxygen demand Biochemical oxygen demand (BOD)- oxidation of an organic compound is carried out by microorganisms using the organic matter as a food source Biossay- to measure by biological means BOD is measured by finding the change in dissolved oxygen concentration before and after bacteria is added to consume organic matter Biochemical oxygen demand Aerobic decomposition- when organisms use oxygen to consume waste The rate at which oxygen is consumed is directly proportional to the concentration of degradable organic matter remaining at any time BOD is a first order reaction L = BOD dL/dt = -kL Lt = Lo e-kt where Lo = ultimate BOD BOD Ultimate BOD- maximum amount of oxygen consumption possible when waste has been completely degraded Numerical value of the rate constant k of BOD depends on: Nature of waste and T Ability of organisms in the system to use the waste Nature of the waste Materials that are rapidly degraded have large BOD constants Materials that degrade slowly are almost undegradable in the BOD test BOD rate constant depends on the relative proportions of the various components Easily degradable organics are more completely removed than less readily degradable organics during wastewater treatment Ability of Organisms to use waste Many organic compounds can be degraded by only a small group of microorganisms The population of organisms that can most efficiently use wastes predominates BOD test should always be conducted with organisms that have been acclimated to the waste This created a rate constant that can be compared to that in the river Temperature Oxygen use speeds up as the temperature increases and slows down as the temperature decreases Oxygen use is caused by the metabolism of microorganisms BOD rate constants depend on: 1) Temperature of receiving water throughout the year 2) Comparing data from various locations at different T values Temperature Eqns The BOD rate constant is adjusted to the temperature of receiving water using this: kT=k20()T-20 • T= temperature of interest (in °C) • kT= BOD rate constant at the temperature of interest(in days -1) • k20= BOD rate constant determined at 20 °C (in days -1) • = temperature coefficient. 5 day Bod test 1) A special 300 mL BOD bottle is filled with a sample of water that has been appropriately diluted and inoculated with microorganisms 2) Blank samples containing only the dilution water are also placed in BOD bottles and sealed 3) The sealed BOD bottles containing diluted samples and blanks are incubated in the dark at 20°C for the desired number of days 4) After five days has elapsed, the samples and blanks are removed from the incubator and the dissolved oxygen concentration in each bottle is measured. Dissolved Oxygen DO If the discharge of oxygendemanding wastes is within the self-purification capacity, the DO is high If the amount of waste increases, it can result in detrimental changes in plant and animal life Aquatic life cannot survive without DO Objective of water quality management is to assess the capability of a stream to absorb waste Do Sag Curve DO concentration dips as oxygen-demanding materials are oxidized and then rises as oxygen is replenished from atmosphere and photosynthesis Major sources of oxygen: Reaeration from the atmosphere Photosynthesis of aquatic plants Factors of oxygen depletion: BOD of waste discharge DO in waste discharge is less than that in the river Nonpoint source pollution Respiration of organisms and aquatic plants Use of Ponds for Water Quality Oxygen Deficit Equation Define deficit D = DOs - DO in mg/L L = ultimate BOD (mg/L) V (dD/dx) = kd L - kr D Where kd = deoxygenation rate constant (day-1) kr = reaeration rate constant (day-1) Since t = x / V, can write the above in time as dD/dt = kd L - kr D (reaeration vs oxygen use) Solution to this eqn gives the DO sag curve Oxygen Deficit Equation At t = 0, D = Da and L = La - Initial values Solving the equation for Dt = deficit at any time t Dt = kdLa e-kd t - e-kr t + Da e-kr t Kr - kd Critical DO Dt = DOs - DO DO X