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wastewater
liquid wastes and wasted transported in water from households, commercial establishments, and industries, as well as storm water and other surface runoff; may contain high concentrations of organic and inorganic pollutants, pathogenic microorganism, as well as toxic chemicals
time line of wastewater
open dumping
collection & open dumping
collection and disposal without treatment
collection and disposal after treatment
collection and treatment for resource recovery and reuse
suspended solids removal options
coarse screens, fine screens
grit chamber
clarification
filtration
chemically enhanced clarification
colloidal and dissolved solids removal
chemical precipitation
membrane filtration
ion exchange
activated carbon adsorption
biodegradable organics removal options
suspended growth processes
attached growth processes
ponds and lagoons
membrane bioreactors
pathogens removal options
chlorination
ozonation
ultraviolet disinfection
nutrients and nitrogen removal options
biological nitrification-denitrification
air stripping
breakpoint chlorination
phosphorus removal options
biological phosphorus removal
chemical precipitation
volatile organic compounds removal options
activated carbon adsorption
air stripping
preliminary and primary treatment steps
wastewater influent→screens→comminutor→grit chamber→primary clarifier
secondary treatment steps
biological reactor → secondary clarifier
sludge treatment steps
gravity thickener → anaerobic digester → centrifuge
clean water act
1972 and 1977 amendments
regulating discharge of pollutants
regulating water quality standards
emerging wastewater treatment issues
rising energy costs
disposal of biosolids
performance and reliability of plants
presence of endocrine disrupting compounds and toxic chemicals in wastewater (PFAS, micro and nano plastics)
scarcity of fresh water
future directions for WW treatment
energy generation: electricity and thermal energy generation from anaerobic digesters
beneficial reuse of biosolids: reuse as fuel and fertilizer
ww reuse
fundamental research and mathematical modeling
reaction kinetics
study of the effects of temp, pressure, and concentration of reactants and products on the rate of a chemical reaction
chemical reactor
tank or vessel where chemical, biological, or biochemical reactions take place, usually in a liquid medium; chemical reactions are the major transformation mechanism
ideal reactors
batch reactor; plug flow reactor (PFR); continuous-flow stirred tank reactors (CSTR)
conversion/removal efficiency
( [A0] - [At] ) / [A0]
material balance
(rate of input) = (rate of output) + (rate of accumulation) - (rate of consumption)
batch reactor
time period for reaction begins just after the reactor is filled and ends just before contents are emptied → rate of input = 0 = rate of output
- rate of consumption = rate of accumulation
plug flow reactor
rate of input = rate of output - rate of consumption (at steady state)
continuous flow stirred tank reactor
rate of input = rate of output - rate of consumption (at steady state)
batch reactor process
materials added to the reactor and mixed for a period of time necessary for the chemical reactions to occur
mixture is removed at the end of the reaction
all fluid elements have the same residence time in the reactor
at any instant, the reactor contents are homogeneous and have a uniform composition
batch reactor uses
liquid phase reactions
bench scale experiments
batch reactor cons
not suitable for commercial scale applications, especially for gas phase reactions
labor costs and material handling costs are high
PFR steps
elements of homogeneous fluid move through the reactor tube as plugs moving parallel to the tube axis
fluid elements discharged in the same sequence as they entered
no longitudinal mixing although lateral mixing may be there
concentration of reactant across any vertical cross section is the same
all fluid elements have same residence time
PFR uses
suitable for continuous gas phase reactions that take place at high pressure and temp
heat transfer is minimized by putting an insulating jacket around the reactor
no moving parts inside reactor
average reaction rate is higher in a PFR as compared to a CSTR with the same volume (except for 0 order rxns)
CSTR steps
reactants flow continuously into the reactor and the product stream is discharged on a continuous basis while the reactor contents are continuously mixed
influent reactant concentration is immediately reduced to final effluent concentration
CSTR uses
simple to construct and easy to control
ease of access to interior surface
mainly used for liquid phase reactions at low or atmospheric pressure
series of CSTRs design equation
ra = ( [A]i - [A](i-1) ) / ti
semi-batch or semi-flow reactor
batch reactor partially filled with one reactant with progressive addition of other reactants till reaction completion
reactiants added at same time but products removed continuously
reactants added intermittently
products removed intermittently
self-purification mechanisms of natural water
physical, chemical, and biological processses
self-purification factors
hydraulic characteristics: volume, rate, turbulence of flow
physical characteristics: bottom and bank material, variations in sunlight and temp
chemical nature of the natural water
physical processes
dilution, sedimentation and resuspension, filtration
dilution
success depends upon discharging relatively small quantities of waste into large bodies of water
sedimentation
sources of suspended solids: domestic ww, industrial ww, runoff from ag activities
solids may be organic, inorganic, or live organism
size from large to colloids
in suspension solids increase turbidity which leads to
reduced light penetration → restricts photosynthetic activity of plants
inhibits vision of aquatic animals
interferes with feeding of aquatic animals that obtain food by filtration
drawbacks of sediment deposits
anaerobic conditions develop and any organics trapped in them will decompose → soluble compounds in the stream
alter the streambed by filling up pore space → creates unsuitable conditions for reproduction of many aquatic organisms
reduce reservoir storage capacities
increase flooding due to channel fill in
filtration
small particles of organic matter or inorganic clays may be filtered out by rocks along the streambed
as water percolates from surface downward into groundwater if the soil layers are deep and fine enough, removes suspended materials
sunlight photolysis
sunlight can directly excite chemicals and degrade them and can also excite dissolved organic matter to produce reactive oxygen species for chemical oxidation
microbial degradation
bacteria can utilize contaminants as carbon sources or nutrients and degrade them
metabolic and co-metabolic pathways
oxidation, reduction, hydrolysis
phytoremediation
in-site restoration process that uses plants to transform, immobilize, and extract contaminants from soils or water
objectives of ww treatment
reduce level of solids, biodegradable organic matter, pathogens, and toxic compounds to meet regulatory limits
infiltration and inflow
includes water that eventually enters the sewer from foundation drains, leaking pipes, submerged manholes, and groundwater infiltration
preliminary treatment
removal of larger suspended solids and inert materials, physiscal processes
unit operations: screens, comminutors/grinders, grit chambers, flow equalization
flow of prelim treatment
trash rack → bar screen → fine screen → comminutor → grit chamber
grit
particle having a d = 0.2mm with a Gs = 2.65 and settling veloctiy = 0.3 m/s
determination of design flow rate depends on
design period (20-25 years)
population prediction
estimation of wastewater flow
estimation of infiltration and infow
variability of ww flow
screens
placed ahead of pumps and used to preclude entrace of materials into treatment plant
trash racks
screens with large openings to exclude larger debris and garbage
consist of rectangular or circular steel bars arranged in parallel fashion with openings 5.1-5.2 cm
coarse or bar screens
clear openings 2.5-7.6cm
manually cleaned screens should be place at angle
mechanically cleaned can be placed vertically
comminutors
shredding devices, grind solids ¼ to 3/8 in
grit chamber types
horizontal flow: channel shaped settling tanks with an effluent weir
aerated: air keeps lighter organics in suspension while heavier grit settle to bottom
vortex: vortex flow pattern generated