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Regulations Basics Online Session #4 Surface Water
Treatment
WELCOME!
This training is presented by RCAC with funding provided by the California State
Water Resources Control BoardDivision of Drinking Water (DDW)
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Your Moderator Today…
Jean Thompson-Ibbeson
Your Moderator Today…
Neil WorthenLas Cruces, NM
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Attendee List
Today’s Materials
Questions?
Text your questions and comments anytime during the session
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Your Trainer Today
John Hamner
Rural Development Specialist –Environmental
Regulations Basics Online Session #4 Surface Water
Treatment
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Regulations Basics OnlineLearning Objectives
Provide Operators with a working knowledge of the California Safe Drinking Water Act
Basic water treatment techniques
Continue to provide safe water to your customers
Today’s Agenda
Background – Importance of surface water treatment standards
Surface Water Treatment Rule (SWTR)
History & development of the SWTR
Treatment Techniques
Monitoring & Reporting
Additional Resources
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Water Treatment History
Earliest recorded treatment of water = 300 BC (boiling, Hippocratic sleeve)
In the 13th century, Egyptian tombs showed water treatment drawings
In 1804 the first recorded citywide
water treatment plant was
installed in Paisley, Scotland
Water Treatment in the USA
Slow sand filters introduced in the United States around 1870
Modern rapid-sand filtration plant built in 1902 at Little Falls, NJ
In 1909, liquid chlorine was used for disinfection of water supplies
Drinking water regulations began developing state by state
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Chlorination History
Surface Water Treatment
All surface water supplies are assumed to contain pathogenic microbial contaminants
Treatment Operators need to be knowledgeable and technically proficient in surface water treatment operations
California Safe Drinking Water Act regulations set the minimum standards for the treatment of surface water supplies
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Poll Time!Question 1: What were you doing in the 70’s?
Do you even remember the 70’s?
In early 1970’s a series of environmental acts are passed by congress
Clean Air Act
Clean Water Act
Formation of the Environmental Protection Agency (EPA)
Safe Drinking Water Act (SDWA)
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EPA Established December 1970
Drinking water program moved from Public Health Service to EPA
First inventory of community water systems in USA is conducted
EPA works towards federal drinking water guidelines
SDWA approved by Congress
Congress approves SDWA in 1974
SDWA goes into effect June 1977
Amended in 1986 and 1996
Amendments are called rules
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Marking Tool
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Any “rules” really annoy you?
Disinfection by Product
Public Notification
Surface Water Treatment
Lead and Copper
RTCR
Arsenic
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The Original SDWA
Original SDWA set standards for:
Microbial contaminants
Ten inorganic chemicals
Six organic pesticides
Turbidity
Radiological contamination
Concept of primacy
1986 Amendments
83 contaminants monitored in 3 years
Additional 25 contaminants every 3 years
Added ground water protection program
Creation of NTNC category water system
Organic chemicals
Public notification
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SDWA 1986 Amendments
Ground Water Under the Direct Influence –GWUDI
Surface water treatment rule
Higher filtered water standards
CT calculations
Effects of 1986 Amendments
Waivers and exemptions from chemical monitoringSystem specific/Statewide information
needed
Lead and copper rule and corrosion controlStates to determine appropriate
treatment
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Poll Time!Question 2: How many lead and copper samples do you take each sampling cycle?
1996 Amendment High Lights
Source Water Protection
Capacity development (TMF)
Consumer Confidence Reports
New, science based contaminant selection
State Revolving Loan Fund (SRF)
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1996 Amendment High Lights
Radon
Arsenic
Cryptosporidium
Sulfate
Disinfection by Products (DBP)
Distribution operator certification
Questions?
Text your questions and comments anytime during the session
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Poll Time!Question 3: How often do you refer to the California SDWA?
CHAPTER 15. DOMESTIC WATER QUALITY AND MONITORING
REGULATIONS
Determines what will be tested for in raw water;
Bacteria
Nitrite/nitrate
Inorganic/organic chemicals
Fluoride
Radioactivity
Secondary standards
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CHAPTER 15. DOMESTIC WATER QUALITY AND MONITORING
REGULATIONS
Determines the Best Available Technology (BAT) for removal of;
Microbial contaminants
Inorganic chemicals
Radionuclides
Organic chemicals
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BAT
CHAPTER 15. DOMESTIC WATER QUALITY AND MONITORING
REGULATIONS
The Best Available Technology (BAT) for removal of these constituents is generally;
Microbial contaminants
Inorganic chemicals
Radionuclides
Organic chemicals
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CHAPTER 15. DOMESTIC WATER QUALITY AND MONITORING
REGULATIONS
Classification of Facilities based on water quality and monitoring;
Bacteria
Nitrite/nitrate
Inorganic/organic chemicals
Fluoride
Radioactivity
Secondary standards
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Add up the points…
Now That This Has Been Established…
Systems have already been assessed
However, system assessments can change due to;
Change in water source
Change in water quality
Change in water regulations
Change in Health Department Staff
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Marking Tool
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What could cause your treatment process to change?
Source quality System demand
Regulations
My DE Technology
Other Science
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Poll Time!Question 4: What type of treatment do you utilize at your facility?
Treatment Techniques
Physical
Conventional filtration
Direct filtration
Slow sand filtration
Bag filters
Membrane filtration
Other (text)
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Treatment Techniques
Chemicals
Pre-disinfection/oxidation
Coagulants/polymers
pH adjustments
Treatment Techniques
Chlorine
Gas, liquid & HTH
Chlorine dioxide
Chloramines
Ultraviolet light
Ozone
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Conventional Water Treatment
1.Coagulation
2.Flocculation
3.Sedimentation
4.Filtration
Chemicals
Flash Mix
Stage 1
Flocculation
Stage 2
Sedimentation
Stage 3
Filtration
Stage 4
Polymer
Solids Recirculation
Basic Water Treatment Plant Flow
UV/Cl2
Oxidizer/coagulant
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Coagulation - Types
Primary coagulants – Neutralize the electrical charge of particles in water, which allows them to clump together (gain weight)
Coagulant aids – Add density to slow settling floc and adds toughness so floc will not break up (shear) in following processes
Coagulants – How they work
Metallic salts:
Create a series of reactions with the water and other ions in the water resulting in floc
Reactions are due to opposing electrical charge of coagulant and particulates
Floc adsorbs to turbidity in the water
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Coagulants – How They Work
Basic Coagulation Chemistry
Coagulation = physical and chemical reaction between alkalinity and coagulant, which forms insoluble floc
Neutral and lower pH waters favor positive floc due to negative charge of particulates
Best pH for coagulation is 5-7
Proper pH must be maintained (residual alkalinity prevents pH from changing)
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Coagulation - Dosage
Dosage is determined by the jar test
Multiple liter jars filled with raw water
Placed on mixer to imitate flash mix
Coagulant added in milligrams (mg)
Water and coagulants mixed
Mixer turned off, observe settleability
Best dosage in mg/L, apply to system
Process Control – Jar Testing
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Flocculation
Flocculation provides a slow, gentle agitation of the water and coagulants
Transforms smaller particles of floc formed by flash mix into larger floc
Rate of floc growth depended on rate at which smaller floc collides
Larger floc more fragile, slow mixing important to reduce shearing
Water slowed to reduce short circuiting
Horizontal Flocculator
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Vertical Flocculator
Sedimentation/Clarification Basins
Removal of settleable solids by gravity
Usually steel or concrete basins
May be rectangular, square or round
Allows water to flow very slowly
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TURBIDITY REMOVAL – Text Box
Why worry about turbidity?
What is turbidity?
Turbidity…Filtration plants remove it
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Conventional Treatment & Disinfection
Process
coagulation
flocculation
sedimentation
filtration
disinfection
Pros
Removal capabilities
Ability to treat source waters of low or inconsistent quality
Conventional Treatment
Cons
Advanced level operator needed
Adequate land
High costs
Sludge disposal
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Filtration - Types
Dual media – bed of sand used as support media, anthracite coal on the top
Multi media – three or more types of media with varying size & specific gravity
Slow sand – water slowly fed through a large bed of sand
Diatomaceous earth (DE) – Under pressure, water is forced through a filter element that is coated with DE
Multi Media
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Membranes – Text Box
Do you use membrane filtration in your system?
If so, what type?
Description of membrane process
Water forced through a porous membrane under pressure while larger molecules are held back
Reverse Osmosis
Microfiltration
Ultrafiltration
Nanofiltration
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How do Membranes Work?
Contaminants such as bacteria and viruses can not pass
through the membrane’s pores
Water molecules and dissolved salts pass freely through the
membrane pores
Semi permeable membrane wall with microscopic pores
Filtration Flow
Filtration flow may be from the outside into the membrane hollow fiber or from the inside to the outside
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Types of DW Membranes
Microfiltration
Ultrafiltration
Reverse Osmosis
Nanofiltration
Fine particulate removal
Dissolved solids removal
Membranes
Microfiltration (MF) and ultrafiltration (UF) are used in water treatment for the removal of the following constituents:
Algae
Bacteria and viruses
Particles
Sediment 84
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Ion Exchange – Nitrates (NO3)
Cause – Nitrates come from human and animal waste
Effect – Nitrate can create methemoglobinemia (blue baby disease) in small children
Treatment – The BAT is ion exchange, coupled with reverse osmosis
Taste And Odor Problems
Cause:
Biological growth – algae, bacteria, diatoms, flagellates and fungi
Treatment/distribution systems – poor housekeeping, chlorine
Environmental – oxygen depletion in reservoirs due to stratification
Pollution – wastewater, industrial wastes, chemical spills, urban runoff and agricultural waste
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Taste And Odor Control
Treatment:
Coagulation, flocculation, sedimentation
Aeration, with volatile gasses and organic compounds only
Air stripping (air diffusers)
Chlorine, chlorine dioxide, potassium permanganate, ozone
PAC (powdered activated carbon) or GAC (granular activated carbon)
Questions?
Text your questions and comments anytime during the session
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Poll Time!Question 5: What type of disinfectant do you utilize at your facility?
Disinfection & Oxidation
Purpose:
To kill or inactivate all pathogens
Taste and odor control
Helps coagulation process
Helps filtration process
Algae control
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Bacteria
Single cell
0.1 to 10 um
Four shapes: spheroid, rod, spiral and filamentous
Viruses
0.01 to 0.1 um
Composed of DNA or RNA with protein coat
Generally very species specific
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Protozoa
Single cell
> 10 um
Primitive to complex structures
Free living and parasitic species
Disinfection Methods
Physical methods
Ultraviolet rays (UV)
Chemical methods
Chlorine
Gas, liquid, HTH
Chloramines
Chlorine dioxide
Ozone
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Chlorine Gas Feed System
Chlorine Products - Liquid
Sodium hypochlorite (bleach) NaOCI
Comes in gallon jugs or bulk
5.25,12.5-15% available chlorine
Explosive when combined with HTH
Ruins clothing
Raises pH of water treated
Fed with hypochlorinator (positive displacement pump)
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Calcium Hypochlorite
ChloraminesCompounds formed by the reaction of
hypochlorous acid with ammonia
Water usually treated, chlorinated and gaseous (or liquid) ammonia added, but can be added before or during chlorine addition
Ammonia is liquefied compressed gas in cylinders or one ton containers or liquid form (most common)
Usually mixed at 3:1 or 4:1 ratio, chlorine to ammonia
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Chlorine Dioxide CIO2
Must be generated on site (unstable) combining sodium chlorite (liquid or powder) and chlorine solutions at low pH
Greenish yellow gas, odorous
Powerful oxidant
Developed to aid in taste and odor issues
Chlorine Dioxide CIO2 - Pros
Lack of TTHM formation
Effective killing bacteria and viruses
Does not combine with ammonia
Oxidizes iron and manganese
Removes color
Taste and odor control
Somewhat effective against cryptosporidium
Does not create carcinogens
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Chlorine Dioxide CIO2 - Cons
Can create chlorates and chlorites which may cause anemia in some folks (unless you add ferrous sulphate)
Gives water distinct taste, undesirable to some
Higher level operator needed
Cat urine odor (with new Carpet)
Ozone (O3)
Bluish, toxic gas with pungent odor
Ozone generated by passing a high voltage between two electrodes allowing the O2 to split, reattach and become O3
Oxygen must be dry, and particle free
Very effective disinfectant, powerful oxidizer
Must be generated on site, not transportable
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Ozone (O3) - Pros
Very effective disinfectant, not proven to be carcinogenic (if no bromide exists)
Also effective for color, taste and odor
Less likely to create disinfection by products, assuming no bromide (creates Bromate)
Improves coagulation process, which lowers chemical cost, reduces sludge disposal and lengthens filter runs
Ozone (O3) - Cons
Equipment is expensive
High electrical costs
Residual does not last
Need to add disinfectant with residual afterwards
Large foot print
Higher level operator needed
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Questions?
Text your questions and comments anytime during the session
Resources
California Drinking Water Regulations http://www.waterboards.ca.gov/drinking_water/certlic/drinkingwater/documents/lawbook/dwregulations-2014-07-01.pdf
Water Board web site
http://www.waterboards.ca.gov/drinking_water/programs/index.shtml
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http://www.waterboards.ca.gov/drinking_water/certlic/drinkingwater/TMF.shtml
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114LINKS TO RESOURCES
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Thank You For Attending!
We look forward to seeing you
in future online classes!
Thank You For Attending!
Neil [email protected]
(575) 527-5372