Waste Water Operator Study Manual

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N

E

W

M

E

X

I

C

O

W

A S T E W A T E R

S

Y S T E M S

O

PERATOR

C

ERTIFICATION

S

TUDY

M

ANUAL

U

TILITY

O

PERATORS

C

ERTIFICATION

P

ROGRAM

S u r f a c e W a t e r Q u a l i t y B u r e a u

New Mexico Environment Department

PO Box 5469

Santa Fe, New Mexico USA 87502

Tel.: (505) 827-2804

Fax.: (505) 827-0160

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(3)

New Mexico

Wastewater Systems

Operator Certification Study

Manual

Prepared By The

Water Utilities Technical Assistance Program

(NMSU DACC WUTAP)

For The

Utility Operators Certification Program

NMED Surface Water Quality Bureau

PO Box 5469

Santa Fe, NM 87502

November, 2007

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I

NTRODUCTION

This wastewater study guide manual was produced by the NMSU DACC WUTAP (New Mexico State University, Doña Ana Community College, Water Utilities Technical Assistance Program) and funded by the NMED - SWQB, UOCP (New Mexico Environment Department - Surface Water Quality Bureau, Utility Operators Certifi cation Program). Members of the WUTAP staff - Robert Gott, Program Coordinator; Robert George & Bernie Garcia, Field Training Specialists; and Nancy Gott, Offi ce Manager - are solely responsible for the writing, editing, and compilation of this manual. The intent of this manual is to provide a document that elaborates on the subject matter listed in the State Certifi cation Need To Know Criteria. This manual will serve a dual purpose in that the operator will have the necessary information needed to study for their State Certifi cation tests as well as an on hand reference manual that can be used to optimize their treatment processes.

This “WASTEWATER SYSTEMS OPERATOR CERTIFICATION STUDY MANUAL” has been created as a tool to assist Wastewater Systems operators in New Mexico in preparation for taking the New Mexico Collection Systems Operator, Small Wastewater Systems Operator, and Wastewater Systems Operator certifi cation exams. There are two classes of Collection Systems Operator certifi cation, two classes of Small Wastewater Systems Operator certifi cation, and four classes of Wastewater System Operator certifi cation. This guide is intended to be a complete reference manual for technical information. Its purpose is to guide the reader to study material for each of the major subject areas for each of the classes. There is no implied claim that this study manual covers every possible point on which an operator may be tested. However, it is intended to be comprehensive in its coverage of the essential information for each exam.

This study manual is divided into sixteen chapters.

Collection Systems exams will include information from Chapters 1 - 4, 8, 16

Small Wastewater Systems exam will include information from Chapters 1 - 9, 11, 15, 16

Advanced Small Wastewater Systems exam will also include information from Chapters 10, 12 - 13 Wastewater Systems Class 1 exam will include information from Chapters 1 - 9, 11, 15 -16

Wastewater System Class 2 exam will include information from Chapters 1 - 9, 11, 14 - 16 Wastewater Systems Class 3 and 4 exams will include information from all sixteen chapters.

The certifi cation exams use several texts as reference manuals for exam topics. Each chapter of the study guide contains references to specifi c chapters of these manuals for those who wish to access more information on the topics covered in that particular section.

Offi ce of Water Programs, California State University, Sacramento,

Operation of Wastewater Treatment Plants, Volume 1, 4th ed. Operation of Wastewater Treatment Plants, Volume 2, 5th ed. Advanced Waste Treatment, 4th ed.

Operation and Maintenance of Collection Systems, Volume 1, 5th_ed. Operation and Maintenance of Collection Systems, Volume 2, 5th ed.

Jenkins, Richard & Daigger, Manual on the Causes and Control of Activated Sludge Bulking and Foaming, 1st_{, 2}nd_{, & 3}rd _eds.

Standard Methods for the Examination of Water and Wastewater, 18th_{, 19}th_{, & 20}th_eds. US EPA, NPDES Reporting Requirements Handbook

State and Federal Environmental Health & Safety Regulations

Special thanks to:

NMED Utility Operators Certifi cation Program for funding, Mike Coffman, Marie Ortiz, the

NMED Point Source Regulation Section, and many others in the Surface Water Quality Bureau that assisted with review of specifi c chapters in the manual.

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N

EW

M

EXICO

E

NVIRONMENT

D

EPARTMENT

S

URFACE

W

ATER

Q

UALITY

B

UREAU

, U

TILITY

O

PERATORS

C

ERTIFICATION

The New Mexico Water Quality Control Commission, through the New Mexico Environment Department (NMED), grants certifi cation for competency to the operators of water and wastewater systems. The Utility Operators Certifi cation Program (UOCP) conducts the testing for certifi cation.

Certain requirements must be met before an operator is eligible to take a certifi cation examination.

An operator begins the process by completing a test application from the Utility Operators Certifi cation Program. Applications will only be accepted if they are submitted at least 30 days prior to the exam date. A certifi cation offi cer will review each application to determine if the operator is eligible to take the requested examination. An application must be submitted every time a test is taken. Examinations are given several times a year at various locations around the state. A fee for each examination must be paid to NMED

Utility Operators Certifi cation Program. A check or

money order for the proper amount as determined in the currently effective Fee Schedule must accompany each exam application.

Certifi cates must be renewed every three years. The renewal date will be the last day of the certifi cate holder’s birthmonth following the third anniversary of the certifi cate. The UOCP also handles renewal of certifi cates. The fee for renewal is determined by an applicant’s level of profi ciency as listed in the currently effective Fee Schedule for each certifi cate. The UOCP maintains training credits for certifi ed operators only. Each operator must keep a record of all training credits earned. A record of current training credits is mailed to each certifi ed operator yearly in July. Anyone who intends to apply for NM certifi cation must include documentation of training credits when the application is submitted. Certifi ed operators that are taking higher level exams may also have to submit training credit documentation to update training record fi les at the UOCP.

All correspondence, including applications, should be mailed to:

NMED - Surface Water Quality Bureau

Utility Operators Certifi cation Program

PO Box 5469

Santa Fe, NM 87502

Please feel free to call the Utility Operators Certifi cation Program to request information on exam application forms, exam dates and locations, or certifi cation and renewal. The telephone number for the offi ce is 505-827-2804. The web site is www.nmenv.state.nm.us/swqb/fot/index.html

I

MPORTANT

F

ACTS

A

BOUT

O

PERATOR

C

ERTIFICATION

An operator, as defi ned by NM Water Quality Control Commission Regulations, is “any person employed by the owner as the person responsible for the operation of all or any portion of a water supply system or wastewater facility. Not included in this defi nition are such persons as directors of public works, city engineers, city managers, or other offi cials or persons whose duties do not include actual operation or direct supervision of water supply systems or wastewater facilities.”

Under the Utility Operator Certifi cation Act, “a certifi ed operator is a person who is certifi ed by the commission as being qualified to supervise or operate one of the classifications of water supply systems or wastewater facilities”. Experience is “actual work experience, full or part-time, in the fi elds of public water supply or public wastewater treatment. Work experience in a related fi eld may be accepted at the discretion of the commission”. Any claim of related experience will be reviewed by the WQCC or its advisory body, the Utility Operators Certifi cation Advisory Board.

The Advisory Board is an appointed “seven-member board from the certifi ed water systems operators and wastewater facility operators to function with the commission to establish qualifi cations of operators, classify systems, adopt regulations and advise the administration of the Utility Operators Certifi cation Act.”

Experience that includes operation, maintenance or repair of water treatment and water distribution systems is accepted based on whether it is full or part-time. The Advisory Board will review and approve experience in other related fi elds, such as commercial plumbing or utility construction. Credit for part-time experience will be based on the percentage of time devoted to actual operation or maintenance. Full time water or wastewater laboratory experience may be counted as operator experience at a rate of 25% of actual experience. The credit for this experience will be determined by review of the Advisory Board.

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B

ASIC

C

ERTIFICATION

R

EQUIREMENTS

Experience Training Credits Education

Class 1/ Small Systems 1 year* 10 HS Grad or GED*

Class 2 2 years* 30 HS Grad or GED*

Class 3 4 years* 50 HS Grad or GED*

Class 4 1 year as Class 3 80 HS Grad or GED

* - See Substitutions

B

ASIC

C

ERTIFICATION

R

EQUIREMENTS

There are three basic requirements an operator must meet to qualify for New Mexico certification. All certified operators must have at least one year of actual experience in operation or maintenance of a public water system. All levels of certifi cation require high school graduation or

GED (see substitutions.) All levels of certifi cation require a

certain number of training credits in water systems O&M or related fi elds.

S

UBSTITUTIONS

One year of additional experience may be substituted for the high school graduation or GED requirement for all classes except Class 4. Education may be substituted for experience or training credits in some cases. The education must be in a water or wastewater related fi eld. One year of vocational education can be substituted for up to one year of experience. Associate’s and Bachelor’s degrees in a related fi eld may be substituted for up to three years of experience and 50 training credit hours, depending on the amount of actual experience. The criteria for substitution of education for experience are as follows:

No more than one year (30 semester hours) of successfully completed college education in a

non-related fi eld may be substituted for an additional six months of the required experience.

One year of approved vocational school in the water

and/or wastewater fi eld may be substituted for only one

additional year of the required experience.

An associate’s degree for a two-year program in an approved school in the water and/or wastewater fi eld and six months of actual experience in that fi eld (which may be accrued before, during, or after the school program) may be substituted for the requirements of any level up to and including Class 2. An associate’s

degree for a two-year program in an approved school

in the water and/or wastewater fi eld and twelve months of actual experience in that fi eld (which may be accrued before, during, or after the school program) may be substituted for the requirements of any level up to and including Class 3.

Completion of at least three years of actual experience in the water and/or wastewater fi eld plus high school

graduation or equivalent, plus 15 semester hours

of successfully completed college education directly related to the water or wastewater field may be substituted for any level up to and including Class 3. A bachelor’s degree for a major directly related to the water or wastewater fi eld plus two years of actual experience in that fi eld may be substituted for any level up to and including Class 3.

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T

ABLE

OF

Temperature Effects

1-3

pH

1-3

M

EASURINGTHE

S

TRENGTHOF

W

ASTEWATER

1-3

MEASURING SOLIDS IN WASTEWATER

1-4

SOLIDS COMPOSITION IN TYPICAL DOMESTIC WASTEWATER

1-5

1-7

P

RIMARY

T

REATMENT

1-7

SECONDARY TREATMENT

1-7

DISINFECTION

1-7

VERVIEW OF

B

ASIC

B

IOLOGICAL

P

RINCIPALS

R

ELATED TO

W

ASTEWATER

T

REATMENT

1-8

N

ITROGEN

C

OMPOUNDSIN

W

ASTEWATER

1-9

C

HAPTER

2: O

PERATOR

S

AFETY

SAFETY CONSIDERATIONS

2-1

OPERATOR SAFETY TRAINING PROGRAMS

2-1

(8)

Shoring

2-1

Shielding

2-2

Sloping (or benching)

2-2

Other Excavation Requirements

2-2

CONFINED SPACE HAZARDS

2-2

ELECTRICAL AND MECHANICAL HAZARDS

2-5

H

AZARDOUS

C

HEMICALS

2-5

NOISE

2-5

PHYSICAL HAZARDS

2-6

INFECTIOUS MATERIALS

2-6

TRAFFIC HAZARDS

2-7

P

ERSONAL

R

ESPONSIBILITY

F

OR

S

AFETY

F

Common Devices Used for Flow Measurement in Pumping Systems

Full Pipes

3-4

Flow Measurement Transmitters and Readout Equipment

3-4

General Units of Measurements

3-4

4-1

W

CHARACTERISTICS OF GRAVITY SEWERS

IPELINE

I

NSTALLATION

4-4

ANHOLES

4-6

4-10

High Velocity Hydraulic Cleaning Machines,

(Jet Rodders)

4-10

P

ERFORMING

C

LEANINGAND

M

AINTENANCE

O

PERATIONS

4-10

RECORDS

4-11

L

IFT

S

TATIONS

4-11

4-17

A

S

-B

UILT

P

LANS

4-17

C

HAPTER

5: W

ASTEWATER

T

REATMENT

P

ONDS

U

SEOF

P

ONDS

5-1

HISTORY OF PONDS IN WASTE TREATMENT

5-1

P

OND

C

LASSIFICATIONSAND

A

PPLICATIONS

5-3

SERIES OPERATION

5-3

5-4

POND PERFORMANCE

5-5

S

TARTINGTHE

P

OND

5-6

D

AILY

O

PERATIONAND

M

AINTENANCE

5-6

S

CUM

C

ONTROL

5-6

ODOR CONTROL

5-6

WEED AND INSECT CONTROL

5-7

Emergent Weeds

5-7

Suspended Vegetation

5-7

Dike Vegetation

5-7

LEVEE MAINTENANCE

5-8

HEADWORKS AND SCREENING

5-8

BATCH OPERATION

5-8

O

PERATING

S

TRATEGY

5-8

M

AINTAIN

C

ONSTANT

W

ATER

E

LEVATIONSINTHE

P

ONDS

5-8

P

URPOSEOF

S

EDIMENTATIONAND

F

LOTATION

6-1

CALCULATION OF CLARIFIER EFFICIENCY

6-3

TYPICAL CLARIFIER EFFICIENCIES

6-4

6-5

TRICKLING FILTER CLARIFIERS

6-6

ACTIVATED SLUDGE CLARIFIERS

6-6

M

AINTENANCE

6-6

SAFETY

6-7

C

OMBINED

S

EDIMENTATION

-D

IGESTION

U

NIT

6-7

PURPOSE OF UNIT

6-7

HOW THE UNIT WORKS

6-7

I

MHOFF

T

ANKS

6-7

PURPOSE OF THE UNIT

6-7

F

ILM

S

ECONDARY

T

REATMENT

T

RICKLING

F

ILTERS

7-1

DESCRIPTION

OF A TRICKLING FILTER

7-1

P

RINCIPLESOF

T

REATMENT

P

ROCESS

7-2

PRINCIPALS OF OPERATION

7-3

CLASSIFICATION OF FILTERS

7-3

STANDARD-RATE FILTERS

7-3

7-5

SLOUGHING

7-5

POOR EFFLUENT QUALITY

7-5

COLD WEATHER PROBLEMS

7-5

M

AINTENANCE

7-6

Bearings and seals

7-6

Distributor Arms

7-6

Underdrains

7-6

SAFETY

7-7

R

OTATING

B

IOLOGICAL

C

ONTACTORS

7-7

OBSERVING THE MEDIA

7-11

BLACK APPEARANCE

7-11

WHITE APPEARANCE

7-11

SLOUGHING

7-11

M

AINTENANCE

7-11

C

HAPTER

8: M

ECHANICAL

S

YSTEMS

C

ENTRIFUGAL

P

UMPS

8-1

I

MPELLER

R

OTATIONAND

C

ENTRIFUGAL

F

ORCE

8-1

CENTRIFUGAL PUMPS

8-2

PROPELLER PUMPS

8-2

VERTICAL WET WELL PUMPS

8-2

P

OSITIVE

D

ISPLACEMENT

P

UMPS

8-5

RECIPROCATING OR PISTON PUMPS

8-5

INCLINE SCREW PUMPS

8-5

PROGRESSIVE CAVITY PUMPS

8-6

C

ENTRIFUGAL

P

UMP

C

OMPONENTS

8-7

A

LIGNMENT

8-9

B

EARINGS

8-10

L

UBRICATION

8-10

P

UMP

C

HARACTERISTIC

C

URVES

8-10

SHUT OFF HEAD

8-11

CHECKING SHUTOFF HEAD

8-11

C

OMMON

Three Phase Motors

8-12

Single Phasing

8-13

(13)

C

HAPTER

9: D

ISINFECTION

C

HLORINE

T

REATMENT

T

ERMS

9-1

C

HLORINE

D

OSAGE

9-1

CHLORINE DEMAND

9-1

CHLORINE RESIDUAL

9-1

FREE CHLORINE RESIDUAL

9-2

COMBINED CHLORINE RESIDUAL

9-2

E

FFECTSOF

T

EMPERATUREAND

P

H

9-2

BREAKPOINT CHLORINATION

9-2

T

ESTING

F

S

AFETY

9-3

CHLORINATOR ROOM

9-3

CHLORINE STORAGE

9-4

CHLORINE CYLINDERS

9-4

HTH H

ANDLING

S

AFETY

9-4

RESPIRATORY PROTECTION

9-4

GAS MASKS

9-4

SELF-CONTAINED BREATHING APPARATUS (SCBA)

PERATION

9-10

C

10-1

MAINTAINING PROPER DISSOLVED OXYGEN AND MIXING LEVELS

10-2

CONTROLLING THE RAS PUMPING RATE

10-2

MAINTAINING THE PROPER MIXED LIQUOR CONCENTRATION

10-2

(14)

T

YPESOF

A

CTIVATED

S

LUDGE

T

REATMENT

P

ROCESSES

10-3

CONVENTIONAL ACTIVATED SLUDGE

10-4

EXTENDED AERATION ACTIVATED SLUDGE

10-4

ACTIVATED SLUDGE PROCESS VARIANTS

10-4

M

ECHANICAL

C

OMPONENTSOF

A

CTIVATED

S

LUDGE

S

YSTEMS

10-5

AERATION SYSTEMS

10-5

Surface Aerators

10-5

Diffused Aeration Systems

10-6

AERATION BLOWERS

10-6

Positive Displacement Blowers

10-6

Turbine Blowers

10-7

Air Flow Meter

10-7

Air Headers

10-8

Diffusers

10-9

Air Filters

10-9

S

AFETY

10-9

SURFACE AERATOR SAFETY CONSIDERATIONS

10-10

MECHANICAL BLOWER SAFETY CONSIDERATIONS

10-10

AIR DISTRIBUTION SYSTEM SAFETY CONSIDERATIONS

10-10

10-13

Settleometer Test

10-14

A

CTIVATED

S

LUDGE

P

ROCESS

C

ONTROL

S

TRATEGIES

10-29

RESPONDING TO PLANT CHANGES

10-30

C

HAPTER

11: S

OLIDS

H

ANDLING

S

OLIDS

H

ANDLING

P

ROCESSES

11-1

D

IGESTION

11-1

ANAEROBIC SLUDGE DIGESTION

PERATIONOF

A

NAEROBIC

D

IGESTERS

11-4

T

ROUBLE

S

HOOTING

A

NAEROBIC

D

IGESTER

P

ROBLEMS

11-4

A

HICKENERS

11-7

BELT FILTER PRESS

11-8

CENTRIFUGATION

11-9

SLUDGE DRYING BEDS

11-11

Sand Drying Beds

11-11

Asphalt Drying Beds

11-11

(16)

S

LUDGE

R

E

-

USEAND

D

ISPOSAL

11-12

L

AND

A

PPLICATIONOF

B

IOSOLIDS

11-12

SURFACE DISPOSAL OF SLUDGE

11-13

LANDFILLING OF SLUDGE

11-13

C

HAPTER

12: T

ERTIARY

T

REATMENT

C

ONSTRUCTED

W

ETLANDS

12-1

THEORY OF OPERATION

12-1

OVERLAND FLOW WETLANDS

12-1

EFFECTIVE USES OF CONSTRUCTED WETLANDS

12-1

WETLANDS OPERATIONS AND MAINTENANCE

12-2

P

ROCESS

C

ONTROL

T

ESTING

12-2

P

HOSPHORUS

R

EMOVAL

12-2

PHOSPHORUS AS A NUTRIENT

12-2

NEED FOR PHOSPHORUS REMOVAL

12-2

TYPES OF PHOSPHORUS REMOVAL SYSTEMS

12-2

L

IME

P

RECIPITATION

12-2

How the Lime Precipitation Process Removes Phosphorus

12-3

Equipment Necessary for Lime Precipitation

12-3

LUXURY UPTAKE

12-3

Wastewater Treatment Units Used

12-4

Basic Principles of Operation

12-4

ALUMINUM SULFATE FLOCCULATION AND PRECIPITATION (SEDIMENTATION)

12-4

C

HAPTER

13: N

ITROGEN

R

EMOVAL

THE NITROGEN CYCLE

13-1

T

HE

N

EEDFOR

O

PERATIONAL

C

ONTROLOF

N

ITRIFICATION

/ D

ENITRIFICATION

13-5

NITRIFICATION

13-5

(17)

C

HAPTER

14: W

ASTEWATER

L

ABORATORY

PURPOSE OF THIS CHAPTER

14-1

I

MPORTANCEOFTHE

L

ABORATORY

14-1

LABORATORY CERTIFICATION

14-1

LABORATORY SAFETY

14-1

B

ASIC

L

ABORATORY

E

QUIPMENTAND

P

ROCEDURES

14-1

WEIGHTS AND MEASURES

14-1

14-2

TEMPERATURE MEASUREMENTS

14-2

14-6

(18)

FECAL COLIFORM MEMBRANE FILTER PROCEDURE

14-15

C

HAPTER

15: S

AMPLINGAND

R

EPORTING

D

ISCHARGE

M

ONITORING

R

EPORTS

(DMRS)

15-1

INSTRUCTIONS FOR COMPLETION

15-1

REVISED/CORRECTED DMRS

15-2

S

ELF

-G

ENERATED

DMR F

ORMS

15-2

N

ON

-C

OMPLIANCE

R

EPORTS

(NCR

S

)

15-2

B

YPASS

/O

VERFLOW

/U

PSET

R

EPORTS

15-5

S

CHEDULES

/R

EPORTS

15-5

S

LUDGE

R

EPORTING

R

EQUIREMENTS

15-5

F

REQUENCYOF

A

NALYSIS

/M

ONITORING

P

ERIOD

15-6

(19)

Land Application & Surface Disposal Forms

15-6

Additional Reporting Requirements

15-6

Completion of DMR Forms

15-6

Production & Use DMR (SLDP)

15-6

Land Application of DMR (SLLA)

15-7

S

URFACE

D

ISPOSAL

DMR (SLSA)

15-9

L

ANDFILLING

DMR (SLDF)

NVALID

T

EST

15-10

R

ETESTS

15-10

TRE

15-10

WET

15-10

M

OST

C

OMMONLY

A

SKED

Q

UESTIONS

15-10

C

HAPTER

16: S

TATEAND

F

EDERAL

R

EGULATIONS

ORIGIN OF ENVIRONMENTAL, SAFETY AND HEALTH REGULATIONS

16-1

F

EDERAL

C

LEAN

W

ATER

A

CT

16-1

N

EW

M

EXICO

E

NVIRONMENTAL

P

ROTECTION

L

EGISLATION

16-2

NMAC, T

ITLE

20, C

HAPTER

6, P

ART

2 16-2

NMAC, TITLE 20, CHAPTER 6, PART 4

16-2

STANDARDS FOR THE USE OR DISPOSAL OF SEWAGE SLUDGE

16-3

O

CCUPATIONAL

S

AFETYAND

H

EALTH

A

DMINISTRATION

(OSHA) R

EGULATIONS

16-4

A

PPENDIX

A: W

ASTEWATER

M

ATH

C

OMMON

E

QUIVALENTS

U

SED

T

O

S

OLVE

W

ASTEWATER

M

ATH

P

ROBLEMS

A-1

A

PPENDIX

B: W

ASTEWATER

M

ATH

F

ORMULAS

U

SEDTO

S

OLVE

W

ASTEWATER

M

ATH

P

ROBLEMS

B-1

A

PPENDIX

C: F

ECAL

C

,

F

LOW

, C

L

2 R

ESIDUAL

&

P

H

D-1

C

ALCULATING

F

ECAL

C

OLIFORM

G

EOMETRIC

M

EAN

D-4

U

SINGTHE

MAL P

ROVISIONTO

D

ETERMINE

R

EPORTABLE

R

ESULTS

D-6

(20)

C

HAPTER

1: I

NTRODUCTION

TO

W

ASTEWATER

C

HARACTERISTICS

&

T

REATMENT

T

HE

D

EFINITIONOF

W

ASTES

There are two routes by which pollutants enter receiving waters: point sources, such as a wastewater treatment plant discharges from an outfall pipe, and non-point sources, such as agricultural and industrial pollution that originates from a widespread discharge. In New Mexico, point source discharges can be made to streams, rivers and lakes or can be made to underground aquifers, because both surface and ground water discharges are common. Wastewater treatment plants, and wastewater treatment plant operators, control point source pollution. Non-point source discharges also occur to both surface and ground waters in New Mexico. Because non-point source pollution is not limited to a single outfall pipe, it is very hard to control.

The type of pollution, and the impairment of the receiving water are related to the type of waste being discharged. The following section discusses some common wastes and what effect they have upon receiving waters if not properly treated.

Sludge and Scum

Sludge and scum are a component of domestic wastewater and some industrial wastewaters. They are primarily organic in nature. If not removed by the wastewater treatment plant, sludge and scum will accumulate on river bottoms and stream banks. Sludge deposits on river bottoms can prevent fish (particularly trout) from being able to spawn. Scum accumulated on stream banks can

(21)

cause odor problems, can harbor infectious diseases and is unsightly.

Organic Waste (in general)

Organic waste, such as fecal and vegetable matter, toilet paper and sugars can cause a series of problems in receiving waters. One problem is oxygen depletion. Many aquatic organisms, including fish, need dissolved oxygen (O₂) to survive. These types of organisms are referred to as aerobes and the environment they live in as aerobic. Much like you and I, aerobic bacteria breath in O₂ and produce carbon di-oxide (CO₂) as a by-product. Natural surface waters typically contain enough dissolved oxygen to support aerobic organisms. Oxygen depletion can occur when aerobic bacteria use excess organic waste discharged into a receiving stream as food. As the aerobic bacteria multiply, they require more and more dissolved oxygen to sustain their growing numbers. When the population of aerobic bacteria grows large enough, they utilize more oxygen than is available in the river. After this happens, they (and most other aerobic organisms) in the river, die.

When all of the dissolved oxygen in a river has been consumed, another type of organism begins to grow in the altered environment. Anaerobic bacteria live in conditions where there is no dissolved oxygen (septic). Anaerobic bacteria breathe by using the oxygen that is chemically combined with other elements, such as sulfate (SO₄). When anaerobic bacteria use the oxygen from sulfate for respiration, hydrogen sulfide (H₂S) gas is released as a byproduct. Hydrogen sulfide, sometimes called sewer gas, smells like “rotten eggs” and is very dangerous due to its explosive, toxic and suffocating characteristics. Oxygen depleted conditions lead to the growth of anaerobic bacteria, which results in odors in receiving waters. Furthermore, anaerobic bacteria release other objectionable by-products, such as organic acids, methane gas and nutrients, all of which can further harm the natural environment in the receiving stream. Because of the chain of events that the discharge of organic waste sets into motion, one of the principal goals of wastewater treatment is to prevent as much of it from getting into receiving waters as possible.

Nutrients

Nutrients are substances that are required for the growth of living plants and animals. Some major nutrients are nitrogen and phosphorous. Both are found in wastewater in various forms. Nitrogen is typically present in influent in the forms of ammonia (NH₃) and organically bound nitrogen. Both nitrogen compounds can be measured by the Total Kjeldahl Nitrogen (TKN) test. Nitrogen may be present in effluent as ammonia, organically bound nitrogen or even nitrite (NO₂) and nitrate (NO₃). Phosphorous is present in influent and effluent primarily in the form of phosphates (PO₄). When large amounts of nutrients are allowed to enter into rivers and lakes, they can cause problems by increasing the growth of plants, such as algae. If the algae growth is extensive, it can choke up the water body. As the lower layers of algae are blocked off from the sun, they die and end up as food for bacteria. This begins the cycle described earlier under “organic waste discharges”, which leads to oxygen depletion.

Toxins

Several substances in wastewater can be toxic if not properly treated. One of these is ammonia. Ammonia is usually the main form of nitrogen present in domestic wastewater, while industrial wastes may or may not contain ammonia. Most people that have owned a fish tank are aware that even small amounts of ammonia can kill aquarium fish. Similarly, large-scale fish kills can occur when effluent-containing ammonia is discharged into receiving waters. In the case of point source discharges, ammonia toxicity depends upon the pH and temperature as well as the dilution factor in the receiving water. Warm temperatures and high pH make ammonia much more toxic to fish. If the discharge is to a small stream where only a little dilution occurs, ammonia can cause serious problems. Another toxin of concern is the residual chlorine that is left over from the disinfection process (this process is discussed further on in this text). If residual chlorine is discharged into a receiving water, even in small amounts, it can also be toxic to fish. For this reason, chlorinated effluents must often be dechlorinated to eliminate all of the measurable residual chlorine.

Last, with regard to toxins, is the problem of ground water contamination from nitrogen compounds such as nitrate (and ammonia that is converted into nitrate by soil bacteria). If nitrate contamination occurs in an aquifer that is used for drinking water, the nitrate could cause methemoglobinemia, also called blue babies syndrome, in infants that drink the water. Methemoglobinemia is a condition where the blood’s ability to carry oxygen is greatly reduced. Recent research has also linked long term consumption of high levels of nitrate to other health problems.

Figure 1.1 - Oxygen Depletion

Reprinted, with permission, from Operation of Wastewater Treatment Plants, Vol. I, 2nd_{ed., Office of Water Programs, California State University,}

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Suspended Solids

Inorganic suspended material like sand, dirt and silt and organic material like sludge both deposit on river bottoms and prevent fish from spawning. In New Mexico, one of the largest non-point source pollution problems is habitat loss caused by suspended solids silting up river bottoms. Point source discharges of sludge and sediment can cause the same problem.

Pathogenic Organisms

Wastewater can potentially contain any disease causing organism, or pathogen, that the people contributing waste to the collection system are infected with. Common diseases caused by water borne pathogens include; typhoid, hepatitis, cholera, dysentery and polio. Pathogens fall into the following categories:

If pathogens are discharged without treatment into the natural environment, they will pose a danger to anyone that is exposed to them. For this reason, one of the primary goals of wastewater treatment is to disinfect the effluent before it is discharged. This can be accomplished by several different methods that rely upon very different principals. These are discussed later in Chapter 9 - Disinfection.

Regardless of the method of disinfection, the test used to measure the effectiveness of disinfection is the same. Because so many varied types of pathogens could be present, it is not practical to perform laboratory test to detect each pathogen. Instead, we use a group of microorganisms that indicates that pathogens could be present.

The group of microorganisms that we use to indicate the level of pathogenic contamination is the Fecal Coliform group. Fecal Coliform are a group of organisms that live in the intestinal tract of all warm blooded animals, including man. If Fecal Coliform are detected in water, it indicates that a warm-blooded animal has defecated into the water and therefore pathogens could be present. Although some members of the Fecal Coliform group are harmful to humans, such as toxin producing strains of Esterichia Coli (E. coli), they are not pathogens. As a whole, we all live quite comfortably as host to the billions, if not trillions, of Fecal Coliform in our intestines.

Temperature Effects

High temperature discharges can disrupt the natural ecology in surface waters by encouraging the growth of algae and aquatic plants that would not normally be as abundant. In addition, seasonal temperature changes can cause the treatment plant to operate less efficiently. This is most evident during cold weather because the growth and activity of the microorganisms in the treatment plant slows down considerably.

pH

pH is a measurement of water’s acid or alkaline condition. pH is measured on a scale that spans from 0 to 14 with 7 being the middle, or neutral value. pH values lower than 7 are progressively acidic while pH values that are higher than 7 are progressively basic, (also called caustic or alkaline). Most living organisms live in a narrow pH range that is near neutral. If an effluent has a pH that is higher or lower than that of the receiving water, the organisms in the receiving water may be killed off. In addition, if the pH of the influent coming into a wastewater treatment plant changes rapidly and significantly, the plant treatment processes may be disrupted.

M

EASURING THE

S

TRENGTHOF

W

ASTEWATER

Because wastewater contains an unknown mixture of organic and inorganic pollutants, it is generally difficult to characterize. One test that is used to measure the overall strength of wastewater is the Biochemical Oxygen Demand (BOD) test. The BOD test measures the amount of oxygen that is consumed while a sample of wastewater is incubated

Table 1.1 - Types of Pathogens

Pathogen Type

Bacteria

Viruses

Protozoa

Examples

Cholera, Shigella, Salmonella

Norwalk, Rotavirus,

Adenovirus

Giardia lamblia,

Cryptosporidium parvum

Figure 1.3 - The pH Scale

Figure 1.2 - Waterborne Diseases

Reprinted, with permission, from Operation of Wastewater Treatment Plants, Vol. I, 2nd_{ed., Office of Water Programs, California State University,}

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at a temperature of 20 °C. During the test, bacteria consume oxygen as they metabolize the organic material in the sample. Oxygen scavenging chemical compounds in the wastewater sample also consume oxygen, although this is typically only a small contribution to the overall oxygen demand. The more organic material and oxygen scavenging chemicals in a sample, the more oxygen will be consumed during the test. The more oxygen consumed, the higher the BOD. This test offers a particularly good way to measure the strength of wastewater because the test determines how much dissolved oxygen will be required to stabilize the waste, thus giving us an indication of what will be needed to treat an influent or what effect an effluent will have upon a receiving stream. (For more information on the BOD test, refer to Chapter 14, Laboratory Procedures).

M

EASURING

S

OLIDSIN

W

ASTEWATER

We have discussed the different types of pollution and even discussed how we measure some of the different aspects of waste, such as BOD and Fecal Coliform. Now we will discuss how we measure solids and how we express their concentration. As we will see, the concentration of solids in typical domestic wastewater is actually quite small when compared to the amount of water present. Because of this, we express concentration in units that are practical to work with - milligrams per liter (mg/L). (See note.)

When we speak of solids in wastewater, we categorize them according to Table 1.2 opposite:

To actually measure the TS of a sample of wastewater we have to evaporate off the water in an oven and then weigh the residue. This residue represents everything (except gasses) that was in the sample, other than water. To determine the TDS we would do the same thing except that we would first filter the sample through a very fine mesh fiberglass filter and then perform the same test on the liquid that passed through the filter. To determine the TSS, we would dry and weigh the filter with the residue trapped on it and then subtract the weight of the filter. We might also want

Figure 1.4 - Imhoff Cone

NOTE:

One million milligrams is equal to one kilogram (2.2 lbs). One liter of pure water weighs one kilogram (at 60° F). Therefore, when you have one milligram of a solid in one liter of water the concentration is one part solid per million parts water (1 ppm). That is why we can use the units of mg/L and ppm interchangeably.

to measure the settleable portion of the TSS, known as Settleable Solids (SS). These are measured by settling a sample in a piece of laboratory glassware known as an Imhoff Cone. SS are reported as a volume (milliliters per liter; ml/L), not as a concentration (mg/L).

It is important to note that some of the TSS will not settle, even when given days or weeks. This non-settleable TSS is known as colloidal material. Colloids will not settle because they are very small and carry similar charges that keep them separated. The like charges on the colloids, which repel each other, overcome gravity’s ability to settle them out.

SOLIDS GROUP

Total Solids (TS)

Total Dissolved

Solids (TDS)

Total Suspended

Solids (TSS)

Everything that is not water

All the solids that cannot be

filtered out of the water

All the solids that can be

filtered out including:

settleable solids and

non-settleable solids (colloids)

Table 1.2 - Solids in Wastewater

Figure 1.5

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S

OLIDS

C

OMPOSITION

I

N

T

YPICAL

D

OMESTIC

W

ASTEWATER

If we could collect a sample of typical domestic wastewater the solids concentrations would be close to the levels shown in Figure 1.5.

As you can see, most of what makes up wastewater is water. In fact, 99.9% of typical domestic wastewater is water. The total solids represent only about 1/10th_of

one percent (0.1%), or 1000mg/L. You can also see that about 20%; (200mg/L) of the solids are made up by the

TSS, of which 130mg/L are settleable and 70 mg/L are non-settleable. THE VAST MAJORITY, (80% OF THE SOLIDS), ARE DISSOLVED.

Some of the dissolved solids in domestic wastewater are organic and some are inorganic. The dissolved organic solids are often measured as dissolved, or soluble, BOD. The majority of this material was added to the wastewater through human use. Most of the dissolved inorganic solids were present when the water was obtained and treated for human consumption (before it became wastewater). The difference between the two types of dissolved solids is important because modern wastewater treatment plants are designed to remove almost all of the organic portion of the TDS but not the inorganic portion of the TDS, which usually passes right through the treatment plant. Generally, inorganic TDS does not cause pollution problems, although there are rivers in New Mexico that have limitations to the amount of overall TDS that can be discharged into them.

T

YPICAL

W

ASTEWATER

T

REATMENT

P

ROCESSES

As we have already discussed, the processes used in a modern wastewater treatment plant are designed to remove most if not all suspended material, including settleable solids and colloidal particles. In addition, dissolved organic solids are removed to a high degree. Finally, pathogenic microorganisms are reduced to prevent the spread of water borne diseases. Separate units within the treatment plant accomplish the removal of different types of solids as well as pathogen reduction. Not all treatment plants employ the same units or treatment methods because there are many ways to accomplish the treatment goals. Location,

economics and even historical precedent affect which types of treatment processes are employed.

Figure 1.6 - Treatment Plant Process Schematic, on the following page shows the common treatment processes and their location in the treatment train. Your treatment plant may differ considerably.

P

RETREATMENT

Wastewater plant pretreatment processes are the first treatment to occur to the wastewater as it enters the plant. Pretreatment usually includes screening, grit removal, flow measurement and pumping.

Screening is accomplished by a barscreen which, as the name implies, is a screen made up of a number of bars arranged in such a way that the trapped material (screenings) can be easily removed. It is important that the screening material be removed so that it does not get caught up in mechanical equipment further on in the treatment plant. The importance of adequate screening for any size wastewater treatment facility CAN NOT be over-emphasized.

Grit removal can be accomplished in several ways. Grit refers to inorganic settleable solids, such as sand, rocks and eggshells. It is an important step in the treatment process because if not removed, grit will accumulate in pipes and tanks later on in the treatment plant. Grit can also cause excessive wear to lift pumps and valves. For this reason, grit removal should take place before the lift pumps whenever possible. The grit and screenings that are removed from the wastewater should be disposed of in

TYPICAL INFLUENT POLLUTANT CONCENTRATIONS

P

ARAMETER

BOD5

TSS

TDS

Settleable Solids

pH

Fecal Coliform

TKN

(Ammonia + Organic Nitrogen)

Nitrate/ Nitrite

Phosphorous

Fats, Oils and

Grease

C

ONCENTRATION

200 mg/L

800 mg/L

10 ml/L

6 – 9

Too Numerous to Count

30 mg/L

< 1.0mg/L

2.0 mg/L

Varies Greatly

E

FFLUENT

G

OAL

< 30 mg/L

< 1000 mg/L

< 0.1 ml/L

6 – 9

< 500 cfu/ 100ml

< 10 mg/L

Total Nitrogen

< 1.0 mg/L

None Visible

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an approved landfill after passing a paint filter test, which ensures no liquid is draining from them.

Flow measurement should be included on the influent side of all treatment plants but is most common in plants with a daily flow of 100,000 gallons or more. It is important to measure not only the daily flow but also the high and low flows so that the true maximum and minimum hydraulic loading is known. This information helps the operator understand what is happening in the treatment plant. Be aware that the flow does not come into most treatment plants at a constant rate. Instead, the flow arrives as peaks and lows that relate to the activity of the people contributing wastewater to the system. The largest peak is typically experienced during the morning hours (following the time when every body wakes up, showers, starts laundry etc). Smaller peaks usually occur after lunch and after dinner. At 3:00 AM there is generally very little flow entering the plant.

Lift pumping is necessary in many treatment plants although some plants receive their flow at a grade that eliminates the need for pumping. If possible, the design engineer should eliminate lift pumps whenever it is practical and cost effective. This is because pumps require significant maintenance and are prone to failure.

P

RIMARY

T

REATMENT

Primary treatment includes sedimentation and floatation. These processes are probably the oldest water treatment methods known to man. In a modern treatment plant, they are accomplished in a primary clarifier. A primary clarifier is a tank, (usually round), where the flow velocity of the wastewater is lowered to the point that suspended solids will settle out and floatable solids will rise to the surface where they can be skimmed off.

The advantage of primary clarification is that 30 – 50% of the influent BOD₅, most of the suspended solids and much of the grease and floatable rubber and plastic product found in influent are removed. The main disadvantage is that the material that has been removed by a primary clarifier, (sludge and scum), must be continuously dealt with. The sludge removed from primary clarifiers is raw and will create odor problems very rapidly unless stabilized (digested). The scum must also be removed and discarded or it will attract vectors (birds, mice, etc.) that could spread infection.

S

ECONDARY

T

REATMENT

Secondary treatment involves physical, chemical and biological processes that convert the dissolved organic

component in the wastewater into settleable solids. Essentially, in secondary treatment we use the dissolved organic material in the influent as food for microorganisms. As the microorganisms consume the organic matter, they convert it into more microorganisms that are then separated from the water by gravity settling. This can be accomplished in many different types of secondary treatment systems such as; trickling filters, rotating biological contactors (RBCs), activated sludge and even lagoons. When using trickling filters, RBCs and activated sludge systems, the microorganisms are grown in one unit and the solids separation occurs in a secondary clarifier. In lagoon systems, the microorganisms grow and settle out all in the lagoon cells.

D

ISINFECTION

After the effluent has been clarified, it is typically disinfected to lower the number of pathogenic microorganisms. This can be done in several ways including; chlorination, ozonation, ultra violet light exposure and even long detention times in lagoon cells. Chlorination is one of the most popular methods of disinfection. However, when chlorine is used to disinfect effluent that is discharged into surface water the effluent must often be de-chlorinated to prevent residual chlorine from harming organisms in the surface water body. This is most often accomplished by adding a sulfur compound that reacts with the chlorine to form inert salts.

E

FFLUENT

F

LOW

M

EASUREMENT

As discussed earlier, it is desirable to measure the influent flow so that the operator will know the plant hydraulic loading. Measurement of the effluent flow is not only desirable but is a requirement of almost any discharge permit. This is because the discharge volume must be known in order to allow the pollutant loading rates to the environment to be calculated. If you discharge one million gallons of effluent with a pollutant concentration of 10 mg/ L, those one million gallons contain a total of 83.4 lbs. of the pollutant. The discharge volume (flow) must be known in order to make this calculation. Because the volume of influent and effluent can be very large, flow is usually expressed as millions of gallons per day (MGD) rather than gallons per day.

S

OLIDS

H

ANDLING

If a wastewater treatment plant is performing properly a large portion of the suspended solids and dissolved organic solids will be removed from the water before it is discharged. These solids remain everyday while the treated water leaves the plant, consequently, they must be dealt with. This aspect of the treatment plant is separate from the wastewater treatment process and is know as solids handling. Solids handling generally involves four

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components: thickening, digestion, dewatering and sludge disposal or re-use.

Thickening is performed to reduce the volume of sludge that must be stored in a digester. Thickening is accomplished by gravity thickeners, centrifuges, belt presses and diffused air floatation (DAF) units.

Digestion involves the breakdown of the solids by aerobic or anaerobic microorganisms. Digestion is done in aerobic (aerated) or anaerobic (heated, mixed, not aerated) digesters.

Dewatering is just as it sounds, removing water from the solids so they occupy less storage space. Dewatering can be accomplished in many ways including; gravity thickeners, drying beds, centrifuges, belt presses and diffused air floatation (DAF) units.

Disposal or Re-use of the solids after they have been digested and dewatered is the final step in the wastewater treatment process. If it is of a high quality and has undergone proper treatment, sludge generated from municipal wastewater treatment plants can be used beneficially as a resource to improve soil quality in various areas including; crop land, landscaping areas and land reclamation sites. If a beneficial use cannot be found, sludge may be disposed of in municipal landfills, surface disposal sites or, as a last resort, incinerated. Various state and federal regulations exist that pertain to sludge disposal and re-use.

O

VERVIEW OF

B

ASIC

B

IOLOGICAL

P

RINCIPALS

R

ELATED TO

W

ASTEWATER

T

REATMENT

Three main oxygen conditions exist that will sustain life and there are three classes of bacteria that survive in these oxygen conditions. Many of the processes in wastewater treatment involve manipulating oxygen conditions to grow certain types of bacteria or to make bacteria function in a specific way. The three oxygen conditions are as follows:

Aerobic - Dissolved oxygen (O₂) is available.

Aerobic bacteria survive by breathing O₂, producing carbon di-oxide (CO₂) and water are the primary by-products.

Anaerobic – No dissolved oxygen is available,

but oxygen is present in the form of sulfate (SO₄). Anaerobic bacteria can utilize the oxygen bound up in sulfate to breath. Hydrogen sulfide (H₂S), carbon di-oxide and water are the main