Title: Drinking Water
1Drinking Water Wastewater Regulation and
Treatment
2Drinking Water Regulations
- 1893 - Interstate Quarantine Act
- Result Prohibition of Common Drinking Cup on
Interstate Carriers created a market for Dixie
cups - 1914 - Microbiological Standard
- 2 coliforms / 100 ml
- 1925 - New Microbiological Standard
- 1 coliform / 100 ml
- 1942 - Maximum Concentrations for Constituents
- Lead Fluoride Arsenic
- Selenium Barium Hexavalent Chromium
- Copper Magnesium Iron Manganese
- Zinc Chloride Sulfate
- Phenolics Total Solids Alkalinity
- Phenol carbolic acid, addition of methyl group
forms cresols, o, m, or p
3Drinking Water Regulations
- 1962 Limits for
- Alkyl benzene sulfonates (synthetic detergents)
- Carbon-chloroform extract (organic residues)
- Adsorption on activated carbon, chloroform
extraction, gravity quantification - Barium Cadmium Cyanide
- Nitrate Silver Radioactivity
- Safe Drinking Water Act of 1974
- Enacted over concern about organic materials in
drinking water - Established Maximum Contaminant Levels (MCLs) for
several substances Enforceable - Federal Guidelines - Secondary MCLs (SMCLs),
Nonenforceable
41975 - National Interim Primary Drinking Water
Regulations
- Amended repeatedly, now include
- Microbiological Contaminants
- Total and Fecal coliforms, E. coli, Turbidity
- Radioactive Contaminants
- Beta/photon emitters, Alpha emitters, Combined
radium - Inorganic Contaminants
- 15 elements or materials
- Synthetic Organic Contaminants including
Pesticides and Herbicides Volatile Organics - 54 compounds and groups of compounds
5Drinking Water Treatment
6Groundwater Treatment Options
7Surface Water Treatment Options
8Drinking Water Treatment Units or Processes
- INTAKES
- AERATION
- COAGULATION FLOCCULATION
- CLARIFICATION
- FILTRATION
- DISINFECTION
- SOFTENING
- TASTE ODOR CONTROL
- IRON MANGANESE REMOVAL
- TRACE METALS ORGANICS
9AERATION(Usually for Groundwater)
- ADDS OXYGEN
- REMOVES
- Carbon Dioxide Hydrogen Sulfide
- Methane Taste Odors
- REMOVAL MAY BE BY
- Oxidation Volatilization
- Iron Manganese Organics
10Coagulation, Flocculation Clarification
- Coagulation changes the electrical charge of
suspended particles and colloids allows
attachment to each other. Coagulants are usually
cations Alum, Ferric Sulfate, Lime (CaO) - Chemical/Physical process of mixing special
purpose chemical from flow and removing the
resulting product - Silts/Clays, Viruses, Bacteria
- Fulvic Humic Acids, Minerals, Organic
Particulates - Flocculation is the agglomeration of particles
into settleable particles - Clarification - sedimentation of floc particles,
allows longer filter runs, settling velocity of
the floc allows particle removal before the water
leaves the basin
11Drinking Water Filtration
- Rapid Sand Filters are most commonly used for
surface water - May be gravity or pressure flow
- Some States prohibit pressure flow
- Fine-to-course (back wash result)
- Course-to-fine (multi-media)
- Anthracite, Sand, Course Garnet, Fine Garnet
- Rapid Sand filters may clean 1 - 2 gpm/ft2
- Alternatives include microscreens, diatomaceous
earth filters, cartridge filters
12DISINFECTION
- CT concept is the current basis for disinfection
theory - CT K
- C disinfectant concentration
- T contact time
- K proportionality constant, variable with
different organisms - Ohio regulation 30 min contact time, 0.2 mg/l
Cl2 residual - Chlorination is most common in the U.S.
- Effective, low cost, proven technology
- Reactions with natural aquatic organics produce
trihalomethanes -- suspected carcinogens - Ozonation is popular in France, Germany, Canada,
and Russia - Chlorine Dioxide gaining acceptance in Europe and
U.S.
13Chlorine Chemistry
- Cl2 H2O -----gt H Cl- HOCl
- HOCl Hypochlorous Acid, is the most active
ingredient, concentration is pH dependent
dissociates to H -OCl - Active against (listed in decreasing order)
- Bacteria Viruses Protozoans (cysts)
- Chlorine reacts with Ammonia (NH3) to produce
mono, di, and trichloroamines - NH2Cl NHCl2 NCl3
14Chlorine Residuals Chlorine Demand
- Free Chlorine Cl2, HOCl, -OCl
- Combined Chlorine Chloramines
- Free Chlorine has strong disinfecting powers but
is quickly dissipated - Combined Chlorine is slower acting but remains in
solution longer and provides longer-term
protection - Chlorine Demand the difference between the
amount of chlorine applied and the amount of
free, combined, or total chlorine remaining at
the end of the contact period - Anything oxidizable can produce a chlorine
demand, including pathogens, organics,
particulates, sulfides, ammonia, etc.
15Alternative Disinfectants
- Ozone
- O3, powerful oxidant, alternative to chlorine
- Effective at low doses
- Expensive (capital and operating costs)
- Produces no residual
- Chlorine Dioxide
- ClO2, an unstable gas, produced at the point of
use from sodium chlorite, NaClO2 - Nearly as effective as chlorine, does not react
with ammonia to produce chloramines, or with
other organics to form trihalomethanes
16BIOFILMS
- In many environments, microorganisms form, and
exist in, complex, protective layers called
biofilms - Biofilms may form in any part of a drinking water
distribution system. Cooling towers can support
robust biofilms. - Disinfectants may be unable to attack or
completely remove the organisms in biofilms - Most biofilms are made up of non-pathogenic
organisms however, pathogens may be protected in
such an environment
17Softening
- Reduction in dissolved calcium and magnesium
reduces deposits in distribution system - scale
formation (CaCO3) - Hard water reacts with soap to form films that
are difficult to remove - Hard water deposits form scale in boilers
- Softening also removes some trace inorganics
Pb, Cd, Ag, Ba, Cr, As, Hg, and Ra - Lime-soda process adds quick lime (CaO) or
hydrated lime Ca(OH)2, precipitating calcium
carbonate (CaCO3) - Ion-exchange removes Ca2 and Mg2 and replaces
them with Na ions often used in homes
18Taste Odor Control
- Very low concentrations of metals, salts, or
organics may produce detectable levels in
sensitive people - iron, copper, manganese, and
zinc, magnesium chloride and bicarbonate,
chlorinated organics fungal and algal
metabolites hydrogen sulfide, other sulfur
compounds - Activated carbon is often very effective in
removing organics - Oxidation (chlorine, chlorine dioxide, ozone)
19- Iron Manganese Removal
- Iron and manganese cause staining and leave
noticeable residuals at very low concentrations - Fe gt0.2 mg/l Mn gt0.1 mg/l
- Iron promotes growth of iron bacteria in mains
that increase friction and power consumption - Oxidation produces less soluble compounds and
precipitation is often used for removal - Trace Metals
- Iron, Cadmium, Lead, Copper, Zinc may come from
the plumbing system others may be from the
aquifer - Corrosion control processes may be the most
effective means of reducing these concentrations
- precipitation of a layer of calcium carbonate
often provides a nonreactive surface
20- Turbidity
- A measure of suspended particulates in water -
clays, microorganisms, organics - Highly turbid waters are difficult to disinfect
because of high demands - large amounts of
materials to be oxidized organisms protected
from exposure to disinfectants - Coagulation and flocculation, and filtration are
common removal methods - Trace Organics
- Solvents, hydrocarbons, etc. may come from the
aquifer - Modified organics may be the result of
disinfection processes - Humic and fulvic acids are poorly defined and are
common in natural waters - TOC and TOX are broad tests of water quality
- Precipitation, filtration, adsorption, and
oxidation may all remove some of the materials
21Fluoridation
- The fluoridation process was very controversial
when initially implemented - Low concentrations (1 - 2 mg/l) of fluoride
provide strong protection against tooth decay - Slightly higher concentrations (gt 4 mg/l) can
cause discoloring of teeth
22- CROSS CONNECTIONS
- Accidental contamination of drinking water can
occur during routine plumbing modification, sewer
backups, floods, earthquakes, careless
homeowners, etc. - FOAMING AGENTS
- Surfactants (the active part of detergents) can
get into surface water through incomplete sewage
treatment - Groundwater sources include septic tank systems
23Nitrate Nitrite
- Nitrate is common in natural waters at 1 to 2
mg/l - Nitrate (NO3) is reduced to nitrite (NO2) in the
digestive system - reduction is more complete in
infants than adults - because of more alkaline
conditions in system - Excess nitrite produces methemoglobinemia in
infants by oxidizing hemoglobin to methemoglobin
which cannot carry oxygen - Nitrosamines formation (suspected carcinogens)
can also occur from nitrate or nitrite
24- TOTAL DISSOLVED SOLIDS
- High TDS may increase corrosivity because of
increase conductance - High sodium may be of health concern
- CORROSIVITY
- Decreases life of plumbing system
- Solubilized metals, perhaps in toxic quantities -
lead and cadmium are of most concern - Copper, iron, and zinc produce tastes and stains
- Corrosion can shield microorganisms from
disinfection processes - Water may be characterized as passive or
aggressive
25CLEAN WATER ACT - Background
- Rivers and Harbors Act of 1899
- Prohibited discharge of refuse without a permit
from the Secretary of the Army - Water Pollution Control Act of 1948
- Gave primary responsibilities to the States
- Provided construction funds, Money never
appropriated - Water Pollution Control Act Amendments of 1956
- Authorized Grants for construction
- Provided funds for research into Health Effects
- Other minor Acts in 1961, 1965, 1966, 1970
26- Federal Water Pollution Control Act - 1972 - PL
92-500 - Goal of fishable/swimmable water
- Construction Grants for Sewage Treatment
Facilities - BPT - Best Practicable Treatment
- BAT - Best Available Treatment
- Concentrated on Oxygen Demand, Suspended Solids
- 1976 - NRDC v. Train - Consent Decree - resulted
in... - Clean Water Act - 1977 - PL 95-217
- Wetlands Resources Act - 1986
- Water Quality Act Amendments of 1987
- Required EPA regulations on storm water runoff
- Required State nonpoint source management programs
27TITLE I -RESEARCH AND RELATED PROGRAMS
- Sec. 101 - Declaration of Goals and Policy --
Objective Restore and maintain the chemical,
physical, and biological integrity of the
Nation's waters. - Goals
- 1. Eliminate pollutant discharges into navigable
waters by 1985. - 2. Interim goal to protect fish, shellfish, and
wildlife and provide for recreation in and on the
water by July 1, 1983. - 3. Prohibit the discharge of toxic pollutants in
toxic amounts.
28TITLE III - STANDARDS AND ENFORCEMENT
- 304 - Information and Guidelines - provides for
development of water quality criteria. Defines
conventional pollutants - including, but not
limited to, biological oxygen demand, suspended
solids, fecal coliforms, and pH, --- specifically
excluded thermal. - 305 - Water Quality Inventory - requires States
to provide a water quality description, an
inventory of point-source dischargers, and an
estimate of costs of improving quality. - 306 - National Standards of Performance -
requires a list of categories of sources and
establishment of new source performance standards
for those categories
29TITLE IV PERMITS AND LICENSES
- Sec 402 - National Pollutant Discharge
Elimination System - (NPDES) establishes
requirements for issuing permits and State
implementation of the program. - Excludes Irrigation return flows, Storm water
runoff from Oil, Gas and Mining operations - Anti-Backsliding - renewed permits must be as
stringent as the original - Storm water is included by October 1, 1993
30ADDITIONS, AMENDMENTS
- LIMITATIONS ON DISCHARGE OF RAW SEWAGE BY NEW
YORK CITY - North River Plant - required to have advanced
preliminary treatment by Aug, 1986 - Red Hook Plant - required advanced preliminary
treatment by Aug, 1987 - BOSTON HARBOR AND ADJACENT WATERS
- Authorization for constructing waste treatment
works for providing secondary treatment
31Oil Pollution Act
- Revised penalties for oil discharges
- Administrative penalties of 125,000 for
violations of regulations or discharges - Civil penalties of 25,000/ day for discharges,
or 1,000/ barrel of oil - Gross negligence or misconduct minimum penalty of
100,000
32CONVENTIONAL POLLUTANTS
- Several are Empirical, derived by
experimentation - Biological Oxygen Demand - test using
microorganisms that measures oxygen uptake over
five days - Suspended Solids - quantified by filtration of a
sample and drying and weighing the filter - Fecal Coliform Bacteria - microbial analysis
dependent upon incubation conditions and
selective media - pH - measured directly
- Oil and Grease - derived by extraction of a water
sample with a solvent and either an infra-red
(IR) measure of the solvent, or a gravimetric
measure of the residue
33Pretreatment Regulations
- Industrial discharges into POTWs (40 CFR 403)
- POTWs with flows gt 5 million gpd, or smaller
POTWs with significant industrial discharges must
establish local pretreatment programs - National standards must be enforced
- Hazardous wastes are the focus of regulation
- Significant industrial users must meet reporting
requirements - Users subject to categorical pretreatment
standards - Users of gt 25,000 gpd of processed wastewater
- Users that make up gt5 average organic capacity
- Other users with a reasonable potential to
adversely effect the POTWs operation
34Wastewater Treatment
- Collection System
- Sewage
- Domestic (sanitary)
- Industrial
- Mixed
- Stormwater
- Separate Systems
- Combined Systems
- Infiltration (20 to 3,000 gal/acre/day)
35Unit Operations Unit Processes
- Unit Operations - Treatment methods using
physical forces - Screening Mixing Flocculation
- Sedimentation Flotation Filtration
- Aeration (gas transfer)
- Unit Processes - Treatment methods using chemical
or biological reactions - Precipitation Adsorption Disinfection
- Biodegradation Nutrient Removal
36Treatment Levels
- Primary Treatment - (preliminary), physical unit
operations - Removal of constituents that cause maintenance or
operational problems -- debris, grit, oil and
grease, - Secondary Treatment - chemical and biological
unit processes - Removal of biodegradable organics and suspended
solids - Tertiary Treatment - (advanced), combinations of
all three methods - Removal of residual nutrients, toxics, specific
contaminants
37Typical Treatment Process
- Bar Grit
- Influent Screen Chamber Primary
- Clarifier
- Anaerobic Activated
- Digester Sludge Unit(s)
-
-
- Disinfection Secondary
- Clarifier
- Effluent
Sludge Disposal
Sludge Return
38Industrial WastewaterTreatment - Differences
- Equalization - hydraulic residence time at least
equal to activated sludge unit, may be several
times longer - Oil Separation
- Dissolved Air Flotation, Dissolved Gas Flotation
- Corrugated Plate Interceptors
- Sludges may be hazardous by regulation
39Design Criteria
- Flow Rate
- Peak Hour Maximum Day
- Maximum Month Minimum Hour
- Minimum Day Minimum Month
- Mass Loading
- Maximum Day Sustained Peaks
- Maximum Month Minimum Month
- Minimum Day
40WastewaterDaily Flow Pattern
41Reactor Types
- Homogeneous Reactions
- Batch Reactor
- Plug-Flow Reactor
- Complete-Mix Reactor, Stirred Tank Reactor
- Complete-Mix Reactors in Series -
- May be significantly more effective than the same
volume in a single unit - Arbitrary -Flow Reactor
- Heterogeneous Reactions
- Packed-Bed Reactor
- Fluidized-Bed Reactor
42Mass-Balance Analysis
- Accumulation Inflow - Outflow Generation
- V dC/dt QCo - QC V(-kC)
- V volume of reactor
- dC/dt rate of change of reactant concentration
within reactor - Q volumetric flow rate into/out of reactor
- Co reactant concentration in influent
- C reactant concentration in reactor and
effluent - k first-order reaction-rate constant
- Mass Balance Applications
- Model constituent biodegradation or removal
(volatilization, precipitation, etc.) - Model solids (sludge) formation
43Common Operational and Design Practices
- Gravity flow through system
- Only pump the water one time
- Parallel units
- Allow operational flexibility and maintenance
- Minimize human contact with materials
44SIMPLIFIED TREATMENT FLOWFairborn Plant
Grit Tanks
Oxidation Ditches
Digesters
Landfill
Sludge Return
Disinfection
Clarifiers
Effluent to Mad River
45Fairborn NPDES Permit Requirements
- Sampling Stations
- Plant Outfall
- Waste Sludge
- Raw Sewage Influent
- Upstream at State Route 235
- Downstream - 200 ft south of lift station at
River Mile 8.6 - Samples
- Composite samples of at least three grab samples
proportionate in volume to the sewage flow rate
at the time of sampling...intervals of at least
30 min., but not more than 2 hours
46FairbornPerformance Statistics
- Average Daily Flow (mgd) 3.795
- Average Influent
- Suspended Solids 198 mg/l
- BOD 143 mg/l
- Ammonia 16 mg/l
- Average Effluent
- Suspended Solids 6 mg/l 97
- BOD 3 mg/l 98
- Ammonia 0.1 mg/l 99