Method 1680: Fecal Coliforms in

Sewage Sludge (Biosolids) by MultipleTube Fermentation using Lauryl

Tryptose Broth (LTB) and EC Medium 

April 2010
U.S. Environmental Protection Agency

Office of Water (4303T)

1200 Pennsylvania Avenue, NW

Washington, DC 20460

EPA-821-R-10-003
iii

Acknowledgments

The contributions of the following persons and organizations to this study are gratefully acknowledged:

Referee Laboratory

• EPA Office of Research and Development, National Risk Management Research Lab: Mark C.

Meckes and Karen M. White

Volunteer Participant Laboratories

• American Interplex: John Overbey and Lizbeth Huggins

• BioVir Laboratories: Rick Danielson and Jim Truscott

• City of Los Angeles Bureau of Sanitation Environmental Monitoring Division: Farhana

Mohamed and Zora Bahariance

• County Sanitation Districts of Los Angeles County: Shawn Thompson and Julie Millenbach

• Environmental Associates: Susan Boutros and John Chandler

• Hampton Roads Sanitation District: Anna Rule and Bob Maunz

• King County Environmental Laboratory: Greg Ma and Bobbie Anderson

• Hoosier Microbiological Laboratories: Don Hendrickson, Keri Nixon, Katy Bilger, and Lindsey

Shelton

• Massachusetts Water Resources Authority: Steve Rhode and Mariya Gofshteyn

• Milwaukee Metropolitan Sewerage District: Jeff MacDonald and Tim O’Neill

• University of Iowa Hygienic Laboratory: Nancy Hall and Cathy Lord

• Utah Department of Health: Sanwat Chaudhuri and Devon Cole

The following facilities provided biosolid matrices for the study:

• Compost Facility, Columbus, OH: Angela Bianco

• Wastewater Treatment Facility, Sturgeon Bay, WI: Todd Maurina

• Wastewater Treatment Facility, Fairfield, OH: Drew Young

• Wastewater Treatment Facility, Mason, OH: Ernie Stickler

• N-Viro Treatment Facility, Toledo, OH: Cindy Drill

Media Photographs

• Mark C. Meckes, NRMRL, US EPA
iv

Disclaimer

Neither the United States Government nor any of its employees, contractors, or their employees make any

warranty, expressed or implied, or assumes any legal liability or responsibility for any third party’s use of

or the results of such use of any information, apparatus, product, or process discussed in this report, or

represents that its use by such party would not infringe on privately owned rights. Mention of trade

names or commercial products does not constitute endorsement or recommendation for use.

Questions concerning this method or its application should be addressed to:

Robin K. Oshiro

Engineering and Analysis Division (4303T)

U.S. EPA Office of Water, Office of Science and Technology

1200 Pennsylvania Avenue, NW

Washington, DC 20460

oshiro.robin@epa.gov or OSTCWAMethods@epa.gov
v

Table of Contents

1.0 Scope and Application . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1

2.0 Summary of Method . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2

3.0 Definitions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2

4.0 Interferences . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3

5.0 Safety . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3

6.0 Equipment and Supplies . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3

7.0 Reagents and Standards . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5

8.0 Sample Collection, Handling, and Storage . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8

9.0 Quality Control . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 10

10.0 Equipment Calibration and Standardization . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 14

11.0 Sample Preparation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 14

12.0 Lauryl Tryptose Broth (LTB) - EC Broth Procedure . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 21

13.0 Verification . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 23

14.0 Data Analysis and Calculations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 24

15.0 Sample Spiking Procedure . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 30

16.0 Method Performance . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36

17.0 Pollution Prevention . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36

18.0 Waste Management . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 37

19.0 References . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 37

20.0 Figures . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 37

21.0 Glossary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 43

1 April 2010

Method 1680: Fecal Coliforms in Sewage Sludge (Biosolids) by

Multiple-Tube Fermentation using Lauryl Tryptose Broth (LTB) and EC

Medium

April 2010

1.0 Scope and Application

1.1 This method describes multiple-tube fermentation procedures [also called the most probable

number (MPN) procedure] for the detection and enumeration of fecal coliform bacteria in

biosolids. These methods use culture-specific media and elevated temperature to isolate and

enumerate fecal coliform organisms. Fecal coliform bacteria, including Escherichia coli (E. coli),

are commonly found in the feces of humans and other warm-blooded animals, and indicate the

potential presence of other bacterial and viral pathogens.

1.2 This method is adapted from method 9221E in Standard Methods for the Examination of Water

and Wastewater, 20th Edition, for the determination of fecal coliform bacteria in a variety of

matrices (Reference 19.1).

1.3 This method is designed to meet the survey and monitoring requirements of U.S. Environmental

Protection Agency (EPA) in regulating the use and disposal of biosolids under 40 CFR Part 503. 

Subpart D of the 503 regulations protects public health and the environment through requirements

designed to reduce the potential for contact with disease-bearing microorganisms (pathogens) in

biosolids applied to land or placed on a surface disposal site.

1.4 Fecal coliform density is expected to correlate with the probability of pathogens present and

document process performance (vector attraction reduction).

1.5 This method may be used to determine the density of fecal coliform bacteria in Class A and Class

B biosolids to satisfy the pathogen reduction requirements of Subpart D of Part 503. A biosolid

sample is classified as Class A if it contains a fecal coliform density below 1,000 MPN/g of total

solids (dry weight basis). A biosolid sample is classified as Class B if the geometric mean fecal

coliform density is less than 2 × 106

 MPN/g of total solids (dry weight basis).

1.6 To satisfy the pathogen reduction monitoring alternatives for Class B biosolids, seven samples of

treated biosolids are collected at the time of use or disposal and the geometric mean fecal

coliform bacterial density of these samples is confirmed not to exceed 2 × 106

 MPN/g of total

solids (dry weight basis). Although the Part 503 regulation does not specify the total number of

samples for Class A biosolids, it is recommended that a sampling event extend over two weeks,

and that at least seven samples be tested to confirm that the mean bacterial density of the samples

is below 1,000 MPN/g of total solids (dry weight basis). The analysis of seven samples increases

the method precision by reducing the standard error caused by inherent variations in biosolid

quality.

1.7 The presence of fecal coliforms may be determined in both Class A and Class B biosolids using

the MPN procedure.

1.8 Any modification of the method beyond those expressly permitted is subject to the application

and approval of alternative test procedures under 40 CFR Parts 136.4 and 136.5.
Method 1680

April 2010 2

1.9 Method 1680 was submitted to interlaboratory validation in Class A and Class B biosolid

matrices. A summary of method performance results from this validation study are provided in

Section 16.0. A comprehensive evaluation of the study results is presented in the validation study

report (Reference 19.2). For method application please refer to Title 40 Code of Federal

Regulation Part 136 (40 CFR Part 136).

Note: Based on the high false positive rates observed for Method 1681 in some matrices, EPA

recommends that laboratories conduct their own matrix-specific comparisons to determine the

most appropriate method (1680 or 1681).

2.0 Summary of Method

2.1 Fecal coliform densities of biosolids may be determined by the MPN procedure.

2.2 MPN procedure (Class A and B)

Method 1680 provides for the enumeration of fecal coliforms in Class A and Class B biosolids

using the most probable number (MPN) procedure. In Method 1680, LTB is used as a

presumptive medium followed by EC as confirmation of fecal coliforms. EC may not be used for

direct isolation from a biosolid sample because prior enrichment in presumptive medium (LTB) is

required for optimum recovery of fecal coliforms. 

2.2.1 Summary of the LTB/EC procedure (see Figure 1 in Section 20.0) [see Sections 11.0

and 12.0 for explanation]

2.2.1.1 A minimum of four sample dilutions are required, while five or more are

preferred. Each sample dilution is inoculated into five test tubes, containing

sterile LTB and an inverted vial (gas production).

2.2.1.2 LTB sample tubes are incubated in a water bath or jacketed incubator at 

35°C ± 0.5°C. After 24 ± 2 hours, the tubes are examined for presumptive

growth and gas production. Gas production is indicated by gas bubble

formation within the inverted-vial. Negative tubes are reincubated for an

additional 24 hours and reassessed. Failure to produce gas in LTB medium

within 48 ± 3 hours is a negative presumptive test. EC tubes are incubated in

a water bath at 44.5°C ± 0.2°C for 24 ± 2 hours. Following growth in LTB,

gas production in EC broth within 24 ± 2 hours is considered a positive fecal

coliform reaction. Failure to produce gas is a negative reaction and indicates

fecal coliform bacteria are not present.

2.2.1.3 A total solids determination is performed on a representative biosolids

sample and is used to calculate MPN/g dry weight. Fecal coliform density is

reported as MPN/g dry weight.

3.0 Definitions

3.1 Fecal coliform bacteria are gram-negative, non-spore-forming rods that are found in the intestines

and feces of humans and other warm-blooded animals. The predominant fecal coliform is E. coli. 

In this method, fecal coliforms are those bacteria that grow and produce gas in LTB within a total

of 48 ± 3 hours after incubation at 35°C ± 0.5°C, and that subsequently ferment lactose and
Method 1680

3 April 2010

produce gas within 24 ± 2 hours in EC broth after incubation at 44.5°C ± 0.2°C. Since coliforms

from other sources often cannot produce gas under these conditions, this criterion is used to

define the fecal component of the coliform group. 

3.2 Class A biosolids contain a fecal coliform density below 1,000 MPN/g of total solids (dry weight

basis). 

3.3 Class B biosolids contain a geometric mean fecal coliform density of less than 2 × 106

 MPN/g of

total solids (dry weight basis). 

3.4 Definitions for other terms are given in the glossary at the end of the method.

4.0 Interferences

4.1 MPN procedure: Since the MPN tables are based on a Poisson distribution, if the sample is not

adequately mixed to ensure equal bacterial cell distribution before portions are removed, the

MPN value will be a misrepresentation of the bacterial density.

5.0 Safety

5.1 The analyst must observe normal safety procedures required in a microbiology laboratory while

preparing, using, and disposing of media, cultures, reagents, and materials, and while operating

sterilization equipment.

5.2 Field and laboratory staff collecting and analyzing environmental samples are under some risk of

exposure to pathogenic microorganisms. Staff should apply safety procedures used for pathogens

to handle all samples.

5.3 Mouth-pipetting is prohibited.

6.0 Equipment and Supplies

6.1 Sterile plastic bags, 1-gallon

6.2 Sterile plastic or glass jars with lids, 1-L

6.3 Sterile auger

6.4 Sterile scoops (do not use curved scoops)

6.5 Ice chest

6.6 Wet ice

6.7 Ice packs, blue ice

6.8 Bubble wrap

6.9 Sterile trowels

6.10 Sterile aluminum foil or kraft paper

6.11 Sterile container, such as a stainless steel or plastic bucket suitable for sample collection

6.12 Flat shovel 

6.13 Dilution bottles, borosilicate glass, screw cap, marked at 99 mL or screw cap, borosilicate glass or

plastic tubes marked at 9 mL
Method 1680

April 2010 4

6.14 Tubes, 16 × 150 mm, borosilicate glass, with loose-fitting aluminum, stainless steel or

autoclavable caps

6.15 Durham tubes or vials, 10 × 75 mm, borosilicate glass

6.16 Tubes, 16 × 100 mm, screw cap, borosilicate glass, with autoclavable plastic caps

6.17 Test tube racks to hold sterile culture tubes

6.18 Pipet container, stainless steel, aluminum or borosilicate glass, for glass pipets

6.19 Pipets, sterile, T.D. bacteriological or Mohr, glass or plastic, wide-tip of appropriate volume

6.20 Pipet bulbs, or automatic pipettor

6.21 Platinum wire inoculation loops, at least 3 mm diameter in suitable holders; or sterile plastic

loops

6.22 Sterile disposable applicator sticks

6.23 Bunsen burner or alcohol burner

6.24 Cornwall syringe, sterile, to deliver at least 5 mL

6.25 Media dispensing pump

6.26 Incubator, water- or air-jacketed, humidity-controlled, microbiological type to hold temperature

at 35.0°C ± 0.5°C

6.27 Gable covered water bath, with circulating system to maintain temperature of 44.5°C ± 0.2°C

6.28 Plastic sterile petri dishes, microbiological grade, 15 mm × 100 mm

6.29 Erlenmeyer flasks, 1-L and 2-L

6.30 Stir bar

6.31 Stir plate

6.32 Sterile blender jars and base

6.33 Water bath maintained at 50°C for tempering agar

6.34 Balance, analytical balance capable of weighing 0.1 mg

6.35 Thermometer, checked against a National Institute of Standards and Technology (NIST) certified

thermometer, or one that meets the requirements of NIST Monograph SP 250-23

6.36 Latex gloves for handling samples

6.37 pH meter

6.38 Vortex mixer

6.39 Flasks, borosilicate glass, screw-cap, 250-2000 mL volume

6.40 Graduated cylinders, 100- to 1000-mL, covered with aluminum foil or kraft paper and sterilized

6.41 Beakers, glass or plastic, assorted sizes

6.42 Steel pan of water, 30" × 26" × 10"

6.43 Autoclave or steam sterilizer capable of achieving 121°C [15 lb pressure per square inch (PSI)]

for 15 minutes

6.44 Crucible or aluminum evaporating dish

6.45 Drying oven maintained at 103°C - 105°C for tempering agar
Method 1680

5 April 2010

7.0 Reagents and Standards

7.1 Reagent-grade chemicals shall be used in all tests. Unless otherwise indicated, reagents shall

conform to the specifications of the Committee on Analytical Reagents of the American Chemical

Society (Reference 19.3). The agar used in preparation of culture media must be of

microbiological grade.

7.2 Whenever possible, use commercial dehydrated culture media.

7.3 Purity of reagent water: Reagent-grade water conforming to specifications in Standard Methods

for the Examination of Water and Wastewater (latest edition approved by EPA in 40 CFR Part

136 or 141, as applicable), Section 9020 (Reference 19.1).

7.4 Phosphate buffered dilution water

7.4.1 Composition of stock phosphate buffer solution:

Potassium dihydrogen phosphate (KH2PO4) 34.0 g

Reagent-grade water 500.0 mL

Preparation: Dissolve KH2PO4 in 500 mL reagent-grade water. Adjust the pH of the

solution to 7.2 with 1 N NaOH, and bring the volume to 1 L with reagent-grade water. 

Sterilize by filtration or autoclave at 121°C (15 PSI) for 15 minutes.

7.4.2 Preparation of stock magnesium chloride (MgCl2) solution: Add 38 g anhydrous MgCl2

or 81.1 g magnesium chloride hexahydrate (MgCl2 • 6H2O) to 1 L reagent-grade water. 

Sterilize by filtration or autoclave at 121°C (15 PSI) for 15 minutes.

7.4.3 After sterilization, store the stock solutions in the refrigerator until used. If evidence of

mold or other contamination appears, the affected stock solution should be discarded and

a fresh solution should be prepared.

7.4.4 Working phosphate buffered dilution water: Mix 1.25 mL of the stock phosphate buffer

and 5 mL of the MgCl2 stock per liter of reagent-grade water. Dispense in appropriate

amounts for dilutions and/or for use as rinse buffer. Autoclave at 121°C (15 PSI) for 15

minutes. Final pH should be 7.0 ± 0.2. The amount of time in the autoclave must be

adjusted for the volume of buffer in the containers and the size of the load.

Note: When test tube racks containing 9.0 mL sterile dilution water are prepared, they are

placed into an autoclavable pan with a small amount of water to contain breakage and

minimize evaporation from the tubes.
Method 1680

April 2010 6

7.5 Heart infusion agar (HIA)

7.5.1 Composition:

Beef heart, infusion from 500 g 10.0 g

Bacto tryptose 10.0 g

Sodium chloride (NaCl) 5.0 g

Bacto agar 15.0 g

Reagent-grade water 1.0 L

7.5.2 Add reagents to 1 L of reagent-grade water, mix thoroughly, and heat to dissolve. Adjust 

pH to 7.4 ± 0.2 with 1.0 N hydrochloric acid or 1.0 N sodium hydroxide. Stir well and

autoclave at 121°C (15 PSI) for 15 minutes. Pour into 15 × 100 mm sterile petri plates. 

Let the media warm to room temperature prior to inoculation. Other general growth

media may be used for quality assurance (QA) (Section 9.0) purposes.

7.6 LTB medium

7.6.1 Composition:

Tryptose 20.0 g

Lactose 5.0 g

Dipotassium hydrogen phosphate (K2HPO4) 2.75 g

Potassium dihydrogen phosphate (KH2PO4) 2.75 g

Sodium chloride (NaCl) 5.0 g

Sodium lauryl sulfate 0.1 g

Reagent-grade water 1.0 L

7.6.2 For single strength (1X) LTB, add reagents to 1 L of reagent-grade water, mix

thoroughly, and heat to dissolve. Adjust pH to 6.8 ± 0.2 with 1.0 N hydrochloric acid or

1.0 N sodium hydroxide. Dispense 10-mL volumes into 25 × 150 mm culture tubes. 1X

TSB will be used for inoculation volumes #1 mL. Autoclave at 121°C (15 PSI) for 15

minutes.

7.6.3 For double strength (2X) LTB, prepare as in Section 7.6.2 but use 500 mL of reagentgrade water instead of 1 L.

Note: 2X LTB is necessary for 10-mL inoculations, to ensure that the 10-mL inoculation

volume does not excessively dilute the media.
Method 1680

7 April 2010

7.7 EC medium

7.7.1 Composition: 

Tryptose or trypticase 20.0 g

Lactose 5.0 g

Bile salts mixture or bile salts No.3 1.5 g

Dipotassium hydrogen phosphate (K2HPO4) 4.0 g

Potassium dihydrogen phosphate (KH2PO4) 1.5 g

Sodium chloride (NaCl) 5.0 g

Reagent-grade water 1.0 L

7.7.2 Add reagents to 1 L of reagent-grade water, mix thoroughly, and heat to dissolve. Adjust

pH to 6.9 ± 0.2 with 1.0 N hydrochloric acid or 1.0 N sodium hydroxide, if necessary.

Prior to sterilization, dispense 10 mL per 16 × 150 mm test tubes, each with an inverted

vial, and sufficient medium to cover the inverted vial half way after sterilization. Close

tubes with metal or heat-resistant plastic caps. Autoclave at 121°C (15 PSI) for 15

minutes. Medium should fill inverted tubes leaving no air spaces.

7.8 Positive control

7.8.1 Obtain a stock culture of E. coli (e.g., ATCC # 25922) as a positive control for LTB and

EC medium. Note: ATCC recommends that no more than 5 transfers be made before

returning to the original culture. This will minimize the chance of contamination during

transfers and genetic shift of the culture. One suggestion is to make your own frozen

seed stock upon receipt of the organism that can be used for future work. For additional

information go to http://www.atcc.org.

7.9 Negative controls

7.9.1 Obtain a stock culture of Enterobacter aerogenes (e.g., ATCC # 13048) as a negative

control for EC medium.

7.9.2 Obtain a stock culture of Pseudomonas (e.g., ATCC # 27853) as a negative control for

LTB.

7.10 The storage times for prepared media used in this method are provided in Table 1.

Table 1. Storage Times for Prepared Media

Media Storage Time

Agar or broth (EC, LTB, and HIA) in loose-cap tubes 2 weeks

Agar or broth (EC, LTB, and HIA) in tightly closed screw-cap tubes 3 months

Poured agar plates (should be stored inverted) 2 weeks

Large volume of agar in tightly closed screw-cap flask or bottle 3 months

Note: If media is refrigerated, remove from refrigerator 1-1.5 hours prior to inoculation, so that it reaches room

temperature prior to use.
Method 1680

April 2010 8

7.11 Milorganite® (CAS 8049-99-8) or equivalent

Milorganite® (heat-dried Class A biosolid) is produced by Milwaukee Metropolitan Sewerage

District. It is available in many home gardening centers. 

Obtain Milorganite® as the reference matrix for initial precision and recovery (IPR) and ongoing

precision and recovery (OPR) analyses. Milorganite® is used as the reference matrix because it

is easily accessible, inexpensive, generally does not contain the analyte of interest, and is of

consistent quality. 

8.0 Sample Collection, Handling, and Storage

8.1 The most appropriate location for biosolid sample collection is the point prior to leaving the

wastewater treatment plant. Samples may be taken from pipes, conveyor belts, bins, compost

heaps, drying beds, and stockpiles.

8.2 Collect samples in sterile, non-toxic glass, or plastic containers with leak-proof lids. All

sampling containers and equipment must be clean and sterile.

8.3 Equipment and container cleaning procedure

8.3.1 Wash apparatus with laboratory-grade detergent and water

8.3.2 Rinse with tap water

8.3.3 Rinse with 10% HCl acid wash 

8.3.4 Rinse with distilled water

8.3.5 Allow to air dry

8.3.6 Cover with foil and autoclave for 15 minutes at 121°C (15 PSI)

8.4 Digester biosolids sampling procedure

8.4.1 Collect digester biosolids sample from the discharge pipe.

8.4.2 Purge the discharge pipe of old biosolids and warm to the digester temperature by

allowing biosolids to flow through the pipe into a container or waste collection device

8.4.3 Position a 1-gallon sterile bag under the flow so that only the sample touches the inside

of the bag. Fill the bag, leaving 0.5 inches of head space in the bag for gas production.

Leaving head room is extremely important when taking samples of biosolids that have

been anaerobically digested. 

8.5 Procedure for sampling conveyor belt biosolid output

8.5.1 Using a sterile scoop, transfer the pressed biosolids directly from the conveyer into a

sterile container, without mixing or transferring to another area. 
Method 1680

9 April 2010

8.5.2 Pack sample into sterile container. Leaving additional head space is not as important as 

in Section 8.4 because there is less gas formation.

8.6 Procedure for sampling from a bin, drying bed, truck bed, or similar container

8.6.1 Remove surface material (upper six inches) and set it aside. Divide the underlying

material to be sampled into four quadrants.

8.6.2 Use a scoop or core the sample if material is deep.

8.6.3 Take a sample from each of the quadrants and combine in a sterile container.

8.6.4 After all the samples have been taken, pour the contents of the container out onto a sterile

surface and mix by folding the sample back onto itself several times.

8.6.5 Reduce the sample size by “coning and quartering.” Divide the container contents into 

four even piles. If sample size is still too large, divide each quarter into quarters and

discard half. Put into a glass or plastic sampling container.

8.6.6 An alternate method to “coning and quartering” is to randomly take a flat shovel full of

biosolids from the contents of the container that has been placed on a sterile surface and

put samples into a sampling container. (Curved scoops have been shown to favor a

certain size particle and should not be used.)

8.7 Record the following in your log book:

8.7.1 Facility name and location

8.7.2 Date

8.7.3 Arrival time

8.7.4 Name of facility and contact

8.8 Record the following onto sample container and in log book when known:

8.8.1 Sample number

8.8.2 Date and time

8.8.3 Sampler name

8.8.4 Sample location

8.8.5 Parameters (e.g., type of analysis, field measurements- pH and temperature) 

8.8.6 Volume

8.8.7 Observations

8.9 Ensure that the chain-of-custody form is filled out.
Method 1680

April 2010 10

8.10 Sample handling: Maintain bacteriological samples at <10°C during transit to the laboratory. Do

not allow the sample to freeze. Use insulated containers to ensure proper maintenance of storage

temperature. Sample bottles should be placed inside waterproof bags, excess air purged, and bags

sealed to ensure that bottles remain dry during transit or storage. Refrigerate samples upon

arrival in the laboratory and analyze as soon as possible after collection. Bring samples to room

temperature before analysis.

8.11 Holding time and temperature limitations: For fecal coliform samples for sewage sludge

(biosolids) only, the holding time is extended to 24 hours for the following sample types using

either EPA Method 1680 (LTB-EC) or 1681 (A-1): Class A composted, Class B aerobically

digested, and Class B anaerobically digested. All other matrices should be analyzed within 8

hours of sample collection, 6 hour maximum transport and 2 hours for sample processing. 

Note: Adherence to sample handling procedures and holding time limits is critical to the

production of valid data. Sample results will be considered invalid if these conditions are not

met.

9.0 Quality Control

9.1 Each laboratory that uses this method is required to operate a formal quality assurance (QA)

program. The minimum requirements of this program consist of an initial demonstration of

laboratory capability through the analysis of positive and negative control samples and blanks

(Sections 9.6 and 9.7). Laboratory performance is compared to the performance criteria specified

in Section 16.0 to determine whether the results of the analyses meet the performance

characteristics of the method. Specific quality control (QC) requirements for Method 1680 are

provided below. General recommendations on QA and QC for facilities, personnel, and

laboratory equipment, instrumentation, and supplies used in microbiological analyses are

provided in Reference 19.4. 

9.2 The minimum analytical QC requirements for the analysis of samples using Method 1680 include

an initial demonstration of laboratory capability through performance of the initial precision and

recovery (IPR) analyses (Section 9.3), ongoing demonstration of laboratory capability through

performance of the ongoing precision and recovery (OPR) analysis (Section 9.4) and matrix spike

(MS) analysis (Section 9.5, disinfected wastewater only), and the routine analysis of positive and

negative controls (Section 9.6), method blanks (Section 9.7), and media sterility checks (Section

9.8). For the IPR, OPR and MS analyses, it is necessary to spike samples with

laboratory-prepared spiking suspensions as described in Section 15.0. 

9.3 Initial precision and recovery (IPR): The IPR analyses are used to demonstrate acceptable

method performance (recovery and precision) and should be performed by each laboratory before

the method is used for monitoring field samples. EPA recommends but does not require that an

IPR be performed by each analyst. IPR samples should be accompanied by an acceptable method

blank (Section 9.7) and appropriate media sterility checks (Section 9.8). The IPR analyses are

performed as follows:

9.3.1 Prepare four, 30-g samples of Milorganite® and spike each sample with E. coli ATCC

# 25922 according to the spiking procedure in Section 15.0. Process and analyze each

IPR sample according to the procedures in Sections 11.0 and 12.0 and calculate the fecal

coliform MPN/g dry weight according to Section 14.0.
Method 1680

11 April 2010

9.3.2 Calculate the percent recovery (R) for each IPR sample using the appropriate equation in

Section 15.7.

9.3.3 Using the percent recoveries of the four analyses, calculate the mean percent recovery

and the relative standard deviation (RSD) of the recoveries. The RSD is the standard

deviation divided by the mean, multiplied by 100.

9.3.4 Compare the mean recovery and RSD with the corresponding IPR criteria in Table 2,

below. If the mean and RSD for recovery of fecal coliforms meet acceptance criteria,

system performance is acceptable and analysis of field samples may begin. If the mean

recovery or the RSD fall outside of the required range for recovery, system performance

is unacceptable. In this event, identify the problem by evaluating each step of the

analytical process, media, reagents, and controls, correct the problem and repeat the IPR

analyses.

Table 2. Initial and Ongoing Precision and Recovery (IPR and OPR) Acceptance Criteria

Performance test LTB/EC acceptance criteria

Initial precision and recovery (IPR)

• Mean percent recovery 

• Precision (as maximum relative standard deviation)

65% - 221%

84%

Ongoing precision and recovery (OPR) as percent recovery 37% - 391%

9.4 Ongoing precision and recovery (OPR): To demonstrate ongoing control of the analytical

system, the laboratory should routinely process and analyze spiked Milorganite® samples. The

laboratory should analyze one OPR sample after every 20 field and matrix spike samples or one

per week that samples are analyzed, whichever occurs more frequently. OPR samples must be

accompanied by an acceptable method blank (Section 9.7) and appropriate media sterility checks

(Section 9.8). The OPR analysis is performed as follows:

9.4.1 Spike a 30-g sample of Milorganite® with E. coli ATCC # 25922 according to the

spiking procedure in Section 15.0. Process and analyze each OPR sample according to

the procedures in Sections 11.0 and 12.0 and calculate the number of fecal coliform

MPN/g dry weight according to Section 14.0.

9.4.2 Calculate the percent recovery (R) for the OPR sample using the appropriate equations 

in Section 15.7. 

9.4.3 Compare the OPR result (percent recovery) with the corresponding OPR recovery

criteria in Table 2, above. If the OPR result meets the acceptance criteria for recovery,

method performance is acceptable and analysis of field samples may continue. If the

OPR result falls outside of the acceptance criteria, system performance is unacceptable. 

In this event, identify the problem by evaluating each step of the analytical process

(media, reagents, and controls), correct the problem and repeat the OPR analysis.

9.4.4 As part of the laboratory QA program, results for OPR and IPR samples should be

charted and updated records maintained in order to monitor ongoing method

performance. The laboratory should also develop a statement of accuracy for Method

1680 by calculating the average percent recovery (R) and the standard deviation of the

percent recovery (sr

). Express the accuracy as a recovery interval from R - 2sr to R + 2sr.
Method 1680

April 2010 12

9.5 Matrix spikes (MS): MS analysis are performed to determine the effect of a particular matrix on

fecal coliform recoveries. The laboratory should analyze one MS sample when biosolid samples

are first received from a source from which the laboratory has not previously analyzed samples. 

Subsequently, 5% of field samples (1 per 20) from a given biosolids source should include a MS

sample. MS samples must be accompanied by the analysis of an unspiked field sample

sequentially collected from the same sampling site, an acceptable method blank (Section 9.7), and

appropriate media sterility checks (Section 9.8). When possible, MS analyses should also be

accompanied by an OPR sample (Section 9.4). The MS analysis is performed as follows:

9.5.1 Prepare two, 30-g field samples that were sequentially collected from the same site.

One sample will remain unspiked and will be analyzed to determine the background or

ambient concentration of fecal coliforms for calculating MS recoveries (Section 9.5.3). 

The other sample will serve as the MS sample and will be spiked with E. coli ATCC #

25922 according to the spiking procedure in Section 15.0.

9.5.2 Select dilutions based on previous analytical results or anticipated levels of fecal

coliforms in the field sample in order to accurately estimate fecal coliform density. 

Neither above or below the detection limit of the method. Section 11.0 includes possible

dilution schemes for both Class A and Class B biosolids. 

9.5.3 Spike the MS sample with a laboratory-prepared suspension as described in Section 15.0. 

Process and analyze the unspiked and spiked field samples according to the procedures in

Sections 11.0 and 12.0.

9.5.4 For the MS sample, calculate the fecal coliform MPN/g dry weight according to Section

14.0 and adjust the density (MPN/g dry weight) based on the ambient concentration of

fecal coliforms observed in the unspiked matrix sample.

9.5.5 Calculate the percent recovery (R) for the MS sample (adjusted based on ambient fecal

coliform in the unspiked sample) using the appropriate equations in Section 15.7.

9.5.6 Compare the MS result (percent recovery) with the appropriate method performance

criteria in Table 3. If the MS recovery meets the acceptance criteria, system performance

is acceptable and analysis of field samples from this biosolid source may continue. If the

MS recovery is unacceptable and the OPR sample result associated with this batch of

samples is acceptable, a matrix interference may be causing the poor results. If the MS

recovery is unacceptable, all associated field data should be flagged.

Table 3. Matrix Spike Precision and Recovery Acceptance Criteria

Performance test LTB/EC acceptance criteria

Class A Biosolids: Matrix spike (MS)

MS percent recovery 30 - 424%

Class B Biosolids: Matrix spike (MS)

MS percent recovery 8 - 709%

Class A Biosolids: Matrix spike, matrix spike duplicate (MS/MSD) 

• Percent recovery for MS/MSD 30 - 424%

• Precision (as maximum relative percent difference of MS/MSD) 150%

Class B Biosolids: Matrix spike, matrix spike duplicate (MS/MSD) 

• Percent recovery for MS/MSD 8 - 709%

• Precision (as maximum relative percent difference of MS/MSD) 125%
Method 1680

13 April 2010

9.5.7 Laboratories should record and maintain a control chart comparing MS recoveries for all

 matrices to batch-specific and cumulative OPR sample results analyzed using Method

1680. These comparisons should help laboratories recognize matrix effects on method

recovery and may also help to recognize inconsistent or sporadic matrix effects from a

particular source. 

9.6 Culture Controls

9.6.1 Negative controls: The laboratory should analyze negative controls to ensure that the 

LTB and EC are performing properly. Negative controls should be analyzed whenever a

new batch of media or reagents is used. On an ongoing basis, the laboratory should

perform a negative control every day that samples are analyzed.

9.6.1.1 Negative controls are conducted by inoculating LTB with a known negative

total coliform species (e.g., Pseudomonas ATCC # 27853) and EC with a

known negative fecal coliform species (e.g., Enterobacter aerogenes ATCC

# 13048) and analyzing as described in Section 12.0. Viability of the

negative controls should be demonstrated using a non-selective media (e.g.,

nutrient agar or tryptic soy agar).

9.6.1.2 If a negative control fails to exhibit the appropriate response, check and/or

replace the associated media or reagents, and/or the negative control, and reanalyze the appropriate negative control. 

9.6.2 Positive controls: The laboratory should analyze positive controls to ensure that the

LTB and EC are performing properly. Positive controls should be analyzed whenever a

new batch of media or reagents is used. On an ongoing basis, the laboratory should

perform a positive control every day that samples are analyzed. An OPR sample (Section

9.4) may take the place of a positive control.

9.6.2.1 Positive controls are conducted by inoculating LTB and EC with a known

positive fecal coliform species (e.g., E. coli ATCC # 25922) and analyzing as

described in Section 12.0.

9.6.2.2 If the positive control fails to exhibit the appropriate response, check and/or

replace the associated media or reagents, and/or the positive control, and

reanalyze the appropriate positive control.

9.7 Method blank. Test a 20-mL sterile dilution water sample in the analytical scheme to verify the

sterility of equipment, materials, and supplies. Absence of growth indicates freedom of

contamination from the target organism. On an ongoing basis, the laboratory should perform a

method blank every day that samples are analyzed.

9.8 Media sterility check. To test sterility of media, subject a representative portion of each

batch to incubation at 35°C ± 0.5°C (LTB) or 44.5°C ± 0.2°C (EC) for 48 ± 3 or 24 ± 2 hours

respectively and observe for growth. With respect to media, a batch is defined as one tube/plate

out of 50 in each lot or one tube/plate, if the lot contains less than 50 tubes/plates. Absence of

growth indicates media sterility. On an ongoing basis, the laboratory should perform a media

sterility check every day that samples are analyzed.
Method 1680

April 2010 14

10.0 Equipment Calibration and Standardization

10.1 Check temperatures in incubators/water baths twice daily, a minimum of four hours apart, to

ensure operation is within stated limits of the method and record daily measurements in incubator

log book.

10.2 Check temperatures in refrigerators/freezers at least once daily to ensure operation is within stated

limits of the method. Record daily measurements in refrigerator/freezer log book.

10.3 Calibrate thermometers and incubators at least annually against an NIST certified thermometer or

one that meets requirements of NIST Monograph SP 250-23 (Reference 19.1). Check mercury

columns for breaks.

10.4 Calibrate the pH meter prior to each use period with the two standards (pH 4.0, 7.0, and 10.0)

closest to the range being tested.

10.5 Calibrate top-loading balances monthly with reference weights of ASTM Class 2.

11.0 Sample Preparation 

11.1 Homogenization

Sample homogenization procedures are based on whether the sample is a liquid or a solid. If

sample is alkaline-stabilized (liquid or solid), adjust the pH as described in Section 11.1.3. 

Liquid samples are generally defined as samples containing #7% total solids (dry weight).

11.1.1 Liquid samples: Homogenize 300 mL of sample in a sterile blender on high speed for one

to two minutes. Adjust the pH to 7.0-7.5 by adding 1.0 N hydrochloric acid or 1.0 N

sodium hydroxide, if necessary. This is the “homogenized” sample. When adjusting the

pH do not exceed the homogenized sample volume by greater than 5% (15 mL).

11.1.2 Solid samples: Weigh out 30.0 ± 0.1 g of well-mixed sample in a sterile dish. Whenever

possible, the sample tested should contain all materials that will be included in the

biosolid. For example, if wood chips are part of the biosolid compost, some mixing or

grinding may be needed to achieve homogeneity before testing. Large pieces of wood

that are not easily ground may be discarded before homogenizing. Transfer the sample to

a sterile blender. Alternatively, the sample may be weighed directly into the sterile

blender jar. Use 270 mL of sterile dilution water (Section 7.4) to rinse any remaining

sample into the blender. Cover and blend on high speed for one minute. This is the

“homogenized” sample. A volume of 1.0-mL of the “homogenized” sample contains 10-1

g of the original sample. Adjust the pH to 7.0-7.5 by adding 1.0 N hydrochloric acid or

1.0 N sodium hydroxide, if necessary.

Note: Do not suspend bacteria in dilution water for more than 30 minutes at room

temperature. Chill on wet ice or at 4°C ± 1°C to slow replication between spiking

samples.

11.1.3 Alkaline-stabilized: The alkaline-stabilized biosolid samples generally have a pH

of approximately 12. Prior to analysis, the alkaline-stabilized biosolid samples must be

neutralized to a pH of approximately 7.5. Do not add lab-prepared spikes to the samples

prior to pH adjustment. 
Method 1680

15 April 2010

11.1.3.1 Adjustment of pH should be done in a fume hood. Prior to adjusting the pH

of the sample, calibrate/standardize the pH meter with pH buffers 7.0 and

10.0. Weigh out 30 g of sample into a sterile 600 mL beaker, add 250 mL of

sterile buffered dilution water and a sterile magnetic stir bar. Place beaker on

a mixing plate, insert pH probe into mixture, begin stirring, and take an

initial pH reading. To minimize the amount of volume added to each sample,

pH should be adjusted using 10 N HCl.

Note: The addition of the 10 N HCl will produce fumes, do not be alarmed. 

The addition of the acid should be done incrementally to ensure that the pH

does not drop instantaneously below 5.0. It is recommended that the pH

adjustment be completed within 10-15 minutes and monitored for an

additional 15 minutes to ensure that the sample is able to maintain a constant

pH of around 7.5. Pour pH adjusted sample into blender jar, use the

remaining sterile buffered dilution water (15 mL) to rinse the beaker twice

and pour rinse water into the blender jar. 

11.2 Dilution and Inoculation

Biosolid samples analyzed for fecal coliforms using this method may require dilution prior to

analysis. An ideal sample volume will yield results that accurately estimate fecal coliform

density. Because fecal coliform concentrations in undiluted samples could easily exceed the

analytical range of this procedure, the laboratory must follow the dilution and inoculation

schemes in Section 11.2.1 (liquid) or 11.2.2 (solid), if necessary additional dilutions may be

analyzed to ensure results obtained are not censored (less-than or greater-than) values. Although

other dilution and inoculation schemes may be used, the first transfer from the “homogenized”

sample should always be 11 mL of homogenized sample to 99 mL dilution water or 10 mL of

homogenized sample to 90 mL dilution water. This will ensure that a sufficient amount of the

original biosolid sample is transferred at the beginning of the dilution scheme. 

Note: Do not suspend bacteria in dilution water for more than 30 minutes at room temperature.

For some transfers, it may be convenient to use a sterile, wide-mouth pipette, capable of

transferring particulate matter. If samples are being spiked, a maximum of 1 hour may elapse

between initial unspiked sample homogenization and analysis of spiked samples.

11.2.1 Class A liquid samples: Four series of five tubes each will contain 1.0, 10-1, 10-2, and

10-3 mL of the original sample. See Figure 2 in Section 20.0 for an overview of this

dilution and inoculation scheme. (For spiked samples, four series of five tubes each will

be used for the analysis with 10-2, 10-3, 10-4, and 10-5 mL of the original sample.) 

11.2.1.1 Dilution

(A) Use a sterile pipette to transfer 11.0 mL of “homogenized” sample

(Section 11.1.1) to 99 mL of sterile dilution water (Section 7.4), cap, and

mix by vigorously shaking the bottle a minimum of 25 times. This is

dilution “A.” One mL of dilution “A” contains 10-1 mL of the original

sample.

(B) Use a sterile pipette to transfer 11.0 mL of dilution “A” to 99 mL of

sterile dilution water, and mix as before. This is dilution “B.” One mL

of dilution “B” is 10-2 mL of the original sample.
Method 1680

April 2010 16

(C) Use a sterile pipette to transfer 11.0 mL of dilution “B” to 99 mL of

sterile dilution water, and mix as before. This is dilution “C.” One mL

of dilution “C” is 10-3 mL of the original sample.

(D) Additional dilutions for analysis of spiked samples.

• Use a sterile pipette to transfer 11.0 mL of dilution “C” to 99 mL of

sterile dilution water, and mix as before. This is dilution “D.” One

mL of dilution “D” is 10-4 mL of the original sample.

• Use a sterile pipette to transfer 11.0 mL of dilution “D” to 99 mL of

sterile dilution water, and mix as before. This is dilution “E.” One

mL of dilution “E” is 10-5 mL of the original sample.

11.2.1.2 Inoculation

(A) Use a sterile pipette to inoculate each of the first series of five tubes with

1.0 mL of the original “homogenized” sample per tube (unspiked

samples only). 

(B) Use a sterile pipette to inoculate each of the second series of tubes with

1.0 mL of dilution “A” (unspiked samples only). This is 10-1 mL of the

original sample. 

(C) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “B” (unspiked or spiked samples). This is 10-2 mL of the

original sample.

(D) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “C” (unspiked or spiked samples). This is 10-3 mL of the

original sample.

(E) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “D” (spiked samples). This is 10-4 mL of the original sample. 

(F) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “E” (spiked samples). This is 10-5 mL of the original sample. 

11.2.1.3 Repeat steps 11.2.1.1 and 11.2.1.2 for the remaining Class A samples. When

inoculations are complete, go to Section 12.3.1.4 to continue the LTB/EC

method.

11.2.2 Class A solid samples: For unspiked samples, four series of five tubes will be used for the

analysis with 1.0, 10-1, 10-2 and 10-3 g of the original sample. The first series of tubes

must contain 2X media. See Figure 3 in Section 20.0 for a summary of this dilution and

inoculation scheme. (For spiked samples, four series of five tubes each will be used for

the analysis with 10-2, 10-3, 10-4, and 10-5 g of the original sample.) 

11.2.2.1 Dilution

(A) A 1.0-mL volume of the “homogenized” sample (Section 11.1.2)

contains 10-1 g of the original sample.
Method 1680

17 April 2010

(B) Use a sterile pipette to transfer 11.0 mL of the blender contents to 99 mL

of sterile dilution water (Section 7.4) and shake vigorously a minimum of

25 times. This is dilution “A.” One mL of dilution “A” contains 10-2 g

of the original sample.

(C) Use a sterile pipette to transfer 11.0 mL of dilution “A” to 99 mL of

sterile dilution water and mix as before. This is dilution “B.” One mL of

dilution “B” contains 10-3 g of the original sample. 

(D) Additional dilutions for analysis of spiked samples:

• Use a sterile pipette to transfer 11.0 mL of dilution “B” to 99 mL of

sterile dilution water, and mix as before. This is dilution “C.” One

mL of dilution “C” contains 10-4 g of the original sample.

• Use a sterile pipette to transfer 11.0 mL of dilution “C” to 99 mL of

sterile dilution water and mix as before. This is dilution “D.” One

mL of dilution “D” contains 10-5 g of the original sample.

11.2.2.2 Inoculation

(A) Use a sterile pipette to inoculate each of the first series of five tubes with

10.0 mL of the “homogenized” sample (unspiked samples only). This

series of tubes must contain 2X media. This is 1.0 g of the original

sample. Since test tubes with inverted vials are being used, shaking is

not practical. Solids that will not separate easily and/or may float should

be submerged into the broth with a sterile loop.

(B) Use a sterile pipette to inoculate each of five tubes with 1 mL of the

“homogenized” mixture (unspiked samples only). This is 10-1 g of the

original sample.

(C) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “A” (unspiked or spiked samples). This is 10-2 g of the original

sample.

(D) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “B” (unspiked or spiked samples). This is 10-3 g of the original

sample.

(E) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “C” (spiked samples). This is 10-4 g of the original sample. 

(F) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “D” (spiked samples). This is 10-5 g of the original sample. 

11.2.2.3 Repeat Sections 11.2.2.1 and 11.2.2.2 for remaining Class A solid samples. 

When inoculations are complete, go to Section 12.3.1.4 to continue the

LTB/EC method.
Method 1680

April 2010 18

11.2.3 Class B liquid samples: For unspiked samples, four series of five tubes each will be used

for the analysis with 10-3, 10-4, 10-5, and 10-6 mL of the original sample (additional

dilutions may be analyzed as necessary). See Figure 4 in Section 20.0 for a summary of

this dilution and inoculation scheme. (For spiked samples, five series of five tubes each

will be used for the analysis with 10-5, 10-6, 10-7, 10-8, and 10-9 mL of the original sample.)

11.2.3.1 Dilution

(A) Use a sterile pipette to transfer 11.0 mL of homogenized sample (from

Section 11.1.1) to 99 mL of sterile dilution water (Section 7.4), cap, and

mix by vigorously shaking the bottle a minimum of 25 times. This is

dilution “A.” One mL of dilution “A” is 10-1 mL of the original sample.

(B) Use a sterile pipette to transfer 11.0 mL of dilution “A” to 99 mL of

sterile dilution water, and mix as before. This is dilution “B.” One mL

of dilution “B” is 10-2 mL of the original sample.

(C) Use a sterile pipette to transfer 11.0 mL of dilution “B” to 99 mL of

sterile dilution water, and mix as before. This is dilution “C.” One mL

of dilution “C” is 10-3 mL of the original sample.

(D) Use a sterile pipette to transfer 11.0 mL of dilution “C” to 99 mL of

sterile dilution water, and mix as before. This is dilution “D.” One mL

of dilution “D” is 10-4 mL of the original sample.

(E) Use a sterile pipette to transfer 11.0 mL of dilution “D” to 99 mL of

sterile dilution water, and mix as before. This is dilution “E.” One mL

of dilution “E” is 10-5 mL of the original sample.

(F) Use a sterile pipette to transfer 11.0 mL of dilution “E” to 99 mL of

sterile dilution water, and mix as before. This is dilution “F.” One mL

of dilution “F” is 10-6 mL of the original sample.

(G) Additional dilutions for analysis of spiked samples:

• Use a sterile pipette to transfer 11.0 mL of dilution “F” to 99 mL of

sterile dilution water, and mix as before. This is dilution “G.” One

mL of dilution “G” is 10-7 mL of the original sample.

• Use a sterile pipette to transfer 11.0 mL of dilution “G” to 99 mL of

sterile dilution water, and mix as before. This is dilution “H.” One

mL of dilution “H” is 10-8 mL of the original sample.

• Use a sterile pipette to transfer 11.0 mL of dilution “H” to 99 mL of

sterile dilution water, and mix as before. This is dilution “I.” One

mL of dilution “I” is 10-9 mL of the original sample.

11.2.3.2 Inoculation

(A) Use a sterile pipette to inoculate each of the first series of five tubes with

1.0 mL of dilution “C” (unspiked samples only). This is 10-3 mL of the

original sample.
Method 1680

19 April 2010

(B) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “D” (unspiked samples only). This is 10-4 mL of the original

sample. 

(C) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “E” (unspiked or spiked samples). This is 10-5 mL of the

original sample. 

(D) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “F” (unspiked or spiked samples). This is 10-6 mL of the

original sample.

(E) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “G” (spiked samples). This is 10-7 mL of the original sample.

(F) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “H” (spiked samples). This is 10-8 mL of the original sample.

(G) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “I” (spiked samples). This is 10-9 mL of the original sample.

11.2.3.3 Repeat Sections 11.2.3.1 and 11.2.3.2 for each remaining Class B sample. 

When inoculations are complete, proceed to Section 12.3.1.4 to continue the

LTB/EC method.

11.2.4 Class B solid samples: For unspiked samples, four series of five tubes each will

contain 10-3, 10-4, 10-5, and 10-6 g of the original sample (additional dilutions may be

analyzed as necessary). See Figure 5 in Section 20.0 for a summary of this dilution and

inoculation scheme. (For spiked samples, five series of five tubes each will be used for

the analysis with 10-5, 10-6, 10-7, 10-8, and 10-9 g of the original sample.) 

11.2.4.1 Dilution

(A) A volume of 1.0-mL of the “homogenized” sample (Section 11.1.2)

contains 10-1 g of the original sample.

(B) Use a sterile pipette to transfer 11.0 mL of the blender contents to 99 mL

of sterile dilution water (Section 7.4) and shake vigorously a minimum of

25 times. This is dilution “A.” One mL of dilution “A” contains 10-2 g

of the original sample.

(C) Use a sterile pipette to transfer 11.0 mL of dilution “A” to 99 mL of

sterile dilution water, and mix as before. This is dilution “B.” One mL

of dilution “B” contains 10-3 g of the original sample.

(D) Use a sterile pipette to transfer 11.0 mL of dilution “B” to 99 mL of

sterile dilution water, and mix as before. This is dilution “C.” One mL

of dilution “C” contains 10-4 g of the original sample.

(E) Use a sterile pipette to transfer 11.0 mL of dilution “C” to 99 mL of

sterile dilution water and mix as before. This is dilution “D.” One mL

of dilution “D” contains 10-5 g of the original sample.
Method 1680

April 2010 20

(F) Use a sterile pipette to transfer 11.0 mL of dilution “D” to 99 mL of

sterile dilution water and mix as before. This is dilution “E.” One mL of

dilution “E” contains 10-6 g of the original sample. 

(G) Additional dilutions for analysis of spiked samples:

• Use a sterile pipette to transfer 11.0 mL of dilution “E” to 99 mL of

sterile dilution water, and mix as before. This is dilution “F.” One

mL of dilution “F” is 10-7 g of the original sample.

• Use a sterile pipette to transfer 11.0 mL of dilution “F” to 99 mL of

sterile dilution water, and mix as before. This is dilution “G.” One

mL of dilution “G” is 10-8 g of the original sample.

• Use a sterile pipette to transfer 11.0 mL of dilution “G” to 99 mL of

sterile dilution water, and mix as before. This is dilution “H.” One

mL of dilution “H” is 10-9 g of the original sample.

11.2.4.2 Inoculation

(A) Use a sterile pipette to inoculate each of the first series of five tubes with

1.0 mL of dilution “B” (unspiked samples only). This is 10-3 g of the

original sample.

(B) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “C” (unspiked samples only). This is 10-4 g of the original

sample. 

(C) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “D” (unspiked or spiked samples). This is 10-5 g of the original

sample. 

(D) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “E” (unspiked or spiked samples). This is 10-6 g of the original

sample.

(E) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “F” (spiked samples). This is 10-7 g of the original sample.

(F) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “G” (spiked samples). This is 10-8 g of the original sample.

(G) Use a sterile pipette to inoculate each of five tubes with 1.0 mL of

dilution “H” (spiked samples). This is 10-9 g of the original sample.

11.2.4.3 When inoculations are complete, go to Section 12.3.1.4 to continue the

LTB/EC method.
Method 1680

21 April 2010

12.0 Lauryl Tryptose Broth (LTB) - EC Broth Procedure

12.1 In this protocol, the Lauryl-Tryptose Broth - EC medium is used to determine fecal coliform

densities in Class A and B biosolid samples. Analysis of seven samples collected at the time of

disposal using this procedure will satisfy the requirements of the monitoring alternative for

demonstrating pathogen reduction in both Class A and Class B biosolids. In Method 1680, LTB

is used as a presumptive medium followed by EC as confirmation of fecal coliforms. EC may not

be used for direct isolation from a biosolid sample because prior enrichment in presumptive

medium (LTB) is required for optimum recovery of fecal coliforms. Precision of the test

increases with increasing numbers of replicates per sample tested. For an overview of the MPN

procedure, refer to Figure 1 in Section 20.0.

12.2 Since sample fecal coliform densities are expected to be variable, it is recommended that at least

seven biosolid samples be analyzed using this method. The geometric mean fecal coliform

density of the seven biosolids samples should not exceed 2 × 106

 MPN/g of total solids (dry

weight basis) to qualify as Class B biosolids. Although there is not a specific number of samples

required for Class A biosolids, it is recommended that a sampling event extend over two weeks

and that at least seven samples be collected and determined to be below 1,000 MPN/g of total

solids (dry weight basis) to qualify as Class A biosolids.

12.3 LTB/EC Procedure

12.3.1 Presumptive phase with LTB medium

12.3.1.1 Prepare LTB media and dispense into tubes as directed in Section 7.6. Note: If

media is refrigerated, remove from refrigerator 1-1.5 hours prior to inoculation,

so that it reaches room temperature prior to use.

12.3.1.2 For each sample, arrange test tubes in four rows of five tubes each (Section

11.2). When 10 mL of sample or dilution is used, tubes should contain 10 mL

of 2X LTB media. Clearly label each row of tubes to identify the sample and

dilution to be inoculated. Note: 2X LTB is needed for 10 mL inoculations, to

ensure that the 10-mL inoculation volume does not excessively dilute the LTB.

12.3.1.3 Dilute and inoculate samples depending on the matrix (i.e. Class A solid, Class

B liquid), as described in Section 11.2.

12.3.1.4 Incubate inoculated tubes at 35°C ± 0.5°C. After 24 ± 2 hours, swirl each tube

gently and examine it for growth and gas production. If no gas has formed,

reincubate for an additional 24 ± 2 hours and reassess. Final assessment should

be within a total of 48 ± 3 hours.

12.3.1.5 For tubes with growth, the presence of gas in inverted vials within 48 ± 3 hours

signifies a positive presumptive reaction.

Note: The presence of gas in the absence of growth is usually due to

mishandling or improper shaking of the tubes after inoculation.

12.3.1.6 For tubes with a positive presumptive reaction, proceed to the confirmation

phase (See Photo 1).
Method 1680

April 2010 22

12.3.2 Confirmation phase for fecal coliforms using EC medium

12.3.2.1 Prepare EC broth tubes as described in Section 7.7. For each positive LTB

tube, one EC tube will be inoculated. Note: If media is refrigerated, remove

from refrigerator 1-1.5 hours prior to inoculation, so that it reaches room

temperature prior to use.

12.3.2.2 Gently shake tubes from presumptive test showing positive reaction.

12.3.2.3 Using a sterile 3- to 3.5-mm-diameter loop or sterile wooden applicator stick,

transfer growth from each positively presumptive LTB tube to corresponding

tubes containing EC broth.

12.3.2.4 Place all EC tubes in a 44.5°C ± 0.2°C water bath within 30 minutes of

inoculation and incubate for 24 ± 2 hours. Maintain water level above the

media in immersed tubes.

12.3.2.5 After incubation, examine each tube for growth and gas production. Gas

production with growth in EC broth at 24 ± 2 hours is considered a positive

fecal coliform reaction (See Photo 1). Failure to produce gas constitutes a

negative reaction. Note: The presence of gas in the absence of growth is

usually due to mishandling or improper shaking of the tubes after inoculation.

12.3.2.6 Record positive and negative reactions for the EC tubes. Calculate MPN / g of

total solids (dry weight) from the number of positive EC tubes as described in

Section 14.0.

Photo 1. In LTB (two tubes on left with silver caps) and EC

(two tubes on right with red caps), fecal coliforms produce

turbidity and gas (tubes 1 and 3, when counting from the

left).

12.4 Total solids determination

12.4.1 Determination of percent dry weight - When sample

results are to be calculated on a dry 

weight basis, a second portion of sample should be weighed at

the same time as the portion used for analytical determination. 

WARNING: The drying oven should be contained in a hood or be vented. Significant 

laboratory contamination may result from drying a heavily contaminated sample. 

12.4.2 Immediately after weighing the sample for microbiological examination, weigh 10-30 g

of the sample into a tarred crucible or aluminum evaporating dish. Dry this aliquot

overnight at 103°C to 105°C. Allow to cool in a desiccator before weighing. Calculate

the % dry weight as follows: 

% dry weight =

g dry sample

x 100

g sample
Method 1680

23 April 2010

13.0 Verification

13.1 Individual biochemical tests including oxidase, citrate, lactose fermentation, indole, ONPG

hydroloysis, methyl red, and Voges-Proskauer may be used to verify positive and negative

results.

13.2 Alternately, commercially available multi-test identification systems may be used to verify

positive and negative results. Such identification systems for Enterobacteriaceae must include

lactose fermentation, F-nitrophenyl-$-D-galactopyranoside (ONPG), and cytochrome oxidase test

reactions.

Note: Due to the high false positive and negative rates, it is recommended that analysts be

required to submit all positive and negative tubes with growth to verification for at least one

biosolid sample for each type of biosolid that the analyst normally evaluates on a monthly basis. 

This should increase analyst proficiency in using these procedures. 

14.0 Data Analysis and Calculations

The estimated density of fecal coliform bacteria, based on the confirmation test using EC, is calculated in

terms of most probable number (MPN). Due to the extreme variability in the solid content of biosolids,

fecal coliform results from biosolid samples are reported as MPN/g total solids (dry weight basis). MPN /

g total solids (dry weight) is calculated in three steps (Sections 14.1, 14.2, and 14.3): 

• Selection of significant dilutions

• Calculation of MPN/mL (wet weight)

• Conversion to MPN/g total solids (dry weight)

The calculation of geometric means is provided in Section 14.4.

14.1 Step 1: Select Significant Dilutions

A dilution refers to the mL (liquid samples) or g (solid samples) of original sample that was

inoculated into each series of tubes. For example, with Class B solid samples (Section 11.2.4),

four, five-tube dilutions are used, with 10-3, 10-4, 10-5, and 10-6 g of the original sample in each

tube. Only three of the four dilution series will be used to estimate the MPN. The three selected

dilutions are called significant dilutions and are selected according to the following criteria.

Examples of significant dilution selections are provided in Table 5, below. For these examples,

the numerator represents the number of positive tubes per sample dilution series and the

denominator represents the total number of tubes inoculated per dilution series.

14.1.1 Choose the highest dilution (the most dilute, with the least amount of sample) giving

positive results in all five tubes inoculated and the two succeeding higher (more dilute)

dilutions (For Table 5, Example A, 10-4 is higher/more dilute than 10-3.)

14.1.2 If the lowest dilution (least dilute) tested has less than five tubes with positive results,

select it and the two next succeeding higher dilutions (Table 5, Examples B and C).

14.1.3 When a positive result occurs in a dilution higher (more dilute) than the three significant

dilutions selected according to the rules above, change the selection to the lowest dilution

(least dilute) that has less than five positive results and the next two higher dilutions

(more dilute) (Table 5, Example D).
Method 1680

April 2010 24

14.1.4 When the selection rules above have left unselected any higher dilutions (more dilute)

with positive results, add those higher-dilution positive results to the results for the

highest selected dilution (Table 5, Example E).

14.1.5 If there were not enough higher dilutions tested to select three dilutions, then select the

next lower dilution (Table 5, Example F). 

14.2 Step 2: Calculate MPN/mL (wet weight)

14.2.1 Obtain the MPN index value from Table 4 using the number of positive tubes in the three

significant dilutions series and calculate MPN/mL using the following equation. The

95% confidence limits may also be obtained from Table 4. Table 4 has been adjusted by

a factor of 10 to eliminate having to multiply the MPN index by 10 in the equation

provided below. 

Note: The example calculated numbers provided in the tables below have been rounded at the end

of each step. If your laboratory recalculates the examples using a spreadsheet and rounds only

after the final calculation, values may be slightly different.

MPN / mL =

MPN Index from Table 4

Largest volume tested in the dilution series used for MPN determination

14.2.2 When using MPN tables other than those provided in this method (e.g. Table 9221:IV, 

Standard Methods for Water and Wastewater, Reference 19.1), additional

steps/calculations are required to determine final reporting value of MPN/g dry weight.

For example, Table 9221:IV MPN index is per 100 mL (MPN/100 mL); which will need

to be converted to MPN/mL . In addition, the MPN index must be multiplied by a factor

of 10 when using the largest volume tested in the dilution series used for MPN

determination.

MPN / 100 mL =

10 × MPN Index from Table 9221:VI

Largest volume tested in the dilution series used for MPN determination

MPN / mL =

MPN/100 mL

100
Method 1680

25 April 2010

Table 4. MPN Index and 95% Confidence Limits for Various Combinations of Positive Results

 When Five Tubes are Used per Dilution a

Combination of

Positives

MPN Index

mL

95% Confidence Limits Combination of

Positives

MPN Index

mL

95% Confidence Limits

Lower Upper Lower Upper

0-0-0 <0.1803 1-3-0 0.83 0.12 1.96

0-0-1 0.18 0.03 0.63 1-3-1 1.04 0.20 2.43

0-0-2 0.36 0.03 1.01 1-3-2 1.25 0.29 2.96

0-0-3 0.54 0.03 1.37 1-3-3 1.47 0.38 3.64

0-0-4 0.72 0.08 1.74 1-3-4 1.69 0.48 4.60

0-0-5 0.91 0.15 2.12 1-3-5 1.91 0.57 5.66

0-1-0 0.18 0.03 0.63 1-4-0 1.05 0.21 2.45

0-1-1 0.36 0.03 1.01 1-4-1 1.27 0.30 3.00

0-1-2 0.55 0.03 1.38 1-4-2 1.48 0.39 3.70

0-1-3 0.73 0.08 1.75 1-4-3 1.70 0.48 4.68

0-1-4 0.91 0.15 2.14 1-4-4 1.93 0.58 5.75

0-1-5 1.10 0.23 2.56 1-4-5 2.15 0.67 6.57

0-2-0 0.37 0.03 1.02 1-5-0 1.28 0.30 3.03

0-2-1 0.55 0.03 1.39 1-5-1 1.50 0.40 3.75

0-2-2 0.74 0.08 1.76 1-5-2 1.72 0.49 4.77

0-2-3 0.92 0.15 2.15 1-5-3 1.95 0.58 5.83

0-2-4 1.11 0.23 2.58 1-5-4 2.17 0.68 6.64

0-2-5 1.29 0.31 3.07 1-5-5 2.40 0.77 7.31

0-3-0 0.56 0.03 1.40 2-0-0 0.45 0.03 1.19

0-3-1 0.74 0.09 1.77 2-0-1 0.68 0.06 1.64

0-3-2 0.93 0.16 2.17 2-0-2 0.91 0.15 2.13

0-3-3 1.12 0.23 2.60 2-0-3 1.15 0.25 2.69

0-3-4 1.30 0.31 3.10 2-0-4 1.39 0.35 3.38

0-3-5 1.49 0.39 3.72 2-0-5 1.64 0.46 4.37

0-4-0 0.75 0.09 1.79 2-1-0 0.68 0.06 1.66

0-4-1 0.94 0.16 2.19 2-1-1 0.92 0.15 2.16

0-4-2 1.12 0.24 2.63 2-1-2 1.16 0.25 2.72

0-4-3 1.31 0.32 3.13 2-1-3 1.41 0.36 3.43

0-4-4 1.50 0.40 3.77 2-1-4 1.66 0.46 4.47

0-4-5 1.69 0.48 4.62 2-1-5 1.92 0.57 5.71

0-5-0 0.94 0.16 2.21 2-2-0 0.93 0.16 2.18

0-5-1 1.13 0.24 2.65 2-2-1 1.18 0.26 2.76

0-5-2 1.33 0.32 3.17 2-2-2 1.43 0.36 3.49

0-5-3 1.52 0.40 3.82 2-2-3 1.68 0.47 4.56

0-5-4 1.71 0.48 4.70 2-2-4 1.94 0.58 5.81

0-5-5 1.90 0.56 5.63 2-2-5 2.21 0.69 6.75

1-0-0 0.20 0.03 0.68 2-3-0 1.19 0.26 2.79

1-0-1 0.40 0.03 1.08 2-3-1 1.44 0.37 3.55

1-0-2 0.60 0.03 1.49 2-3-2 1.70 0.48 4.67

1-0-3 0.81 0.11 1.91 2-3-3 1.97 0.59 5.91

1-0-4 1.01 0.19 2.36 2-3-4 2.23 0.70 6.83

1-0-5 1.22 0.28 2.87 2-3-5 2.51 0.82 7.59

1-1-0 0.40 0.03 1.09 2-4-0 1.46 0.38 3.61

1-1-1 0.61 0.03 1.50 2-4-1 1.72 0.49 4.77

1-1-2 0.81 0.11 1.92 2-4-2 1.99 0.60 6.00

1-1-3 1.02 0.19 2.38 2-4-3 2.26 0.72 6.92

1-1-4 1.23 0.28 2.90 2-4-4 2.54 0.83 7.68

1-1-5 1.44 0.37 3.54 2-4-5 2.82 0.94 8.36

1-2-0 0.61 0.03 1.51 2-5-0 1.74 0.50 4.88

1-2-1 0.82 0.12 1.94 2-5-1 2.01 0.61 6.10

1-2-2 1.03 0.20 2.40 2-5-2 2.29 0.73 7.00

1-2-3 1.24 0.29 2.93 2-5-3 2.57 0.84 7.76

1-2-4 1.46 0.38 3.59 2-5-4 2.86 0.95 8.45

1-2-5 1.67 0.47 4.51 2-5-5 3.15 1.07 9.10 a

 Table was developed using the MPN calculator developed by Albert Klee
Method 1680

April 2010 26

Table 4. MPN Index and 95% Confidence Limits for Various Combinations of Positive Results

 When Five Tubes are Used per Dilution (cont.) a

Combination of

Positives

MPN Index

mL

95% Confidence Limits Combination of

Positives

MPN Index

mL

95% Confidence Limits

Lower Upper Lower Upper

3-0-0 0.79 0.10 1.88 4-3-0 2.71 0.90 8.09

3-0-1 1.06 0.21 2.46 4-3-1 3.26 1.11 9.34

3-0-2 1.35 0.33 3.23 4-3-2 3.86 1.32 10.60

3-0-3 1.65 0.46 4.40 4-3-3 4.51 1.54 11.92

3-0-4 1.96 0.59 5.89 4-3-4 5.21 1.76 13.31

3-0-5 2.29 0.73 6.99 4-3-5 5.93 1.96 14.77

3-1-0 1.07 0.22 2.50 4-4-0 3.35 1.14 9.53

3-1-1 1.37 0.34 3.29 4-4-1 3.98 1.37 10.84

3-1-2 1.67 0.47 4.52 4-4-2 4.66 1.59 12.23

3-1-3 1.99 0.60 6.01 4-4-3 5.39 1.81 13.68

3-1-4 2.32 0.74 7.10 4-4-4 6.15 2.02 15.21

3-1-5 2.67 0.88 8.00 4-4-5 6.93 2.23 16.81

3-2-0 1.38 0.35 3.35 4-5-0 4.11 1.41 11.11

3-2-1 1.70 0.48 4.64 4-5-1 4.83 1.64 12.56

3-2-2 2.02 0.62 6.13 4-5-2 5.59 1.87 14.09

3-2-3 2.36 0.76 7.20 4-5-3 6.39 2.09 15.70

3-2-4 2.71 0.90 8.10 4-5-4 7.22 2.30 17.39

3-2-5 3.08 1.04 8.94 4-5-5 8.06 2.50 19.16

3-3-0 1.72 0.49 4.77 5-0-0 2.40 0.76 7.63

3-3-1 2.05 0.63 6.24 5-0-1 3.14 1.06 9.08

3-3-2 2.40 0.77 7.31 5-0-2 4.27 1.46 11.42

3-3-3 2.76 0.92 8.21 5-0-3 5.78 1.92 14.46

3-3-4 3.13 1.06 9.06 5-0-4 7.59 2.39 18.16

3-3-5 3.52 1.20 9.89 5-0-5 9.53 1.65 22.34

3-4-0 2.09 0.64 6.36 5-1-0 3.29 1.12 9.40

3-4-1 2.44 0.79 7.42 5-1-1 4.56 1.56 12.02

3-4-2 2.81 0.93 8.33 5-1-2 6.31 2.07 15.53

3-4-3 3.19 1.08 9.18 5-1-3 8.39 2.57 19.85

3-4-4 3.58 1.23 10.02 5-1-4 10.62 3.04 24.85

3-4-5 3.99 1.37 10.86 5-1-5 12.93 3.04 30.90

3-5-0 2.48 0.80 7.53 5-2-0 4.93 1.67 12.76

3-5-1 2.86 0.95 8.44 5-2-1 7.00 2.24 16.94

3-5-2 3.25 1.10 9.31 5-2-2 9.44 2.80 22.13

3-5-3 3.65 1.25 10.17 5-2-3 12.05 3.31 28.43

3-5-4 4.07 1.40 11.03 5-2-4 14.79 3.81 37.14

3-5-5 4.50 1.54 11.89 5-2-5 17.67 5.03 52.30

4-0-0 1.30 0.31 3.11 5-3-0 7.92 2.47 18.86

4-0-1 1.66 0.46 4.45 5-3-1 10.86 3.08 25.44

4-0-2 2.07 0.64 6.31 5-3-2 14.06 3.68 34.45

4-0-3 2.53 0.82 7.64 5-3-3 17.50 4.34 51.31

4-0-4 3.02 1.02 8.81 5-3-4 21.22 5.29 67.98

4-0-5 3.55 1.21 9.96 5-3-5 25.27 8.14 79.71

4-1-0 1.69 0.48 4.60 5-4-0 12.99 3.48 31.08

4-1-1 2.12 0.66 6.46 5-4-1 17.24 4.29 49.75

4-1-2 2.58 0.85 7.79 5-4-2 22.12 5.63 70.87

4-1-3 3.10 1.05 8.98 5-4-3 27.81 8.82 86.00

4-1-4 3.65 1.25 10.16 5-4-4 34.54 11.59 101.10

4-1-5 4.25 1.45 11.38 5-4-5 42.56 14.37 118.00

4-2-0 2.16 0.67 6.61 5-5-0 23.98 7.62 76.29

4-2-1 2.64 0.87 7.94 5-5-1 34.77 11.72 101.60

4-2-2 3.17 1.08 9.15 5-5-2 54.22 17.91 141.90

4-2-3 3.75 1.29 10.37 5-5-3 91.78 26.72 220.10

4-2-4 4.38 1.50 11.64 5-5-4 160.90 38.37 410.30

4-2-5 5.04 1.71 12.97 5-5-5 >160.90 a

 Table was developed using the MPN calculator developed by Albert Klee
Method 1680

27 April 2010

Examples of MPN/mL calculations are provided in Table 5.

Table 5. Examples of Significant Dilution Selection and Calculation of MPN/mL a

Example

(liquid 

or solid)

10-3 

mL or g 

10-4

mL or g

10-5

mL or g

10-6

mL or g

Step 1:

Significant

Dilutions

Step 2:

(MPN from Table 2 / largest sig. dilution)

= MPN / mL wet weight

A 5/5 5/5 3/5 0/5 5-3-0 (7.92 / 10-4) = 79,200 MPN / mL

79,000 MPN / mL

B 4/5 5/5 1/5 0/5 4-5-1 (4.8 3/ 10-3) = 4830 MPN / mL

4800 MPN / mL

C 0/5 1/5 0/5 0/5 0-1-0 (0.18 / 10-3) = 180 MPN / mL

D 5/5 3/5 1/5 1/5 3-1-1 (1.37 / 10-4) = 13,700 MPN / mL

14, 000 MPN / mL

E 4/5 4/5 0/5 1/5 4-4-1 (3.98 / 10-3) = 3980 MPN / mL

4000 MPN / mL

F 5/5 5/5 5/5 2/5 5-5-2 (54.22 / 10-4) = 542,200 MPN / mL

540,000 MPN / mL a

 Significant dilutions are underlined and largest significant dilutions highlighted

14.3 Step 3: Convert to MPN/g Total Solids (dry weight)

For analysis and calculation of percent total solids see Section 12.4. 

For the conversion to MPN/g total solids (dry weight), we assume that, 

MPN/mL wet weight = MPN/g wet weight.

Therefore, we may convert to MPN/g total solids (dry weight) using the following equation:

MPN / g (dry weight) =

MPN/mL (wet weight) from step 2

Percent total solids (expressed as a decimal)
Method 1680

April 2010 28

Examples of the conversion to MPN/g (dry weight) are provided in Table 6.

Table 6. Examples of Conversion to MPN/g Total Solids (Dry Weight), Continuing From Step 2 in Table 5

Example

(liquid or solid)

Total

Solids

Step 3:

(MPN / mL wet weight from step 2) / percent total solids = MPN / g dry weight

A 4% 79,000 / 0.04 = 1,975,000 = 2.0 x 106

 MPN / g dry weight

B 60% 4800 / 0.6 = 8000 = 8.0 x 103 MPN / g dry weight

C 56% 180 / 0.56 = 321 = 3.2 x 102 MPN / g dry weight

D 22% 14,000 / 0.22 = 63,636 = 6.4 x 104 MPN / g dry weight

E 18% 4,000 / 0.18 = 22,222 = 2.2 x 104 MPN / g dry weight

F 43% 540,000 / 0.43 = 1,255,814 = 1.3 x 106

 MPN / g dry weight

14.4 Calculation of Geometric Mean

To satisfy pathogen reduction requirements for Class B biosolids in Subpart D of Part 503, seven

biosolid samples are collected and the geometric mean density of fecal coliforms is calculated. 

The geometric mean is calculated by:

• converting each sample’s MPN fecal coliforms/g (dry weight) to the log10 value, 

• averaging the log10 values, and

• taking the antilog of the mean log10 value.

An example is provided in Table 7.

Table 7. Calculation of Geometric Mean Fecal Coliform Density for Biosolid Samples

Sample No. MPN Fecal coliforms / g (dry weight) log10

1 600,000 = 6.0 X 105 5.78

2 4,200,000 = 4.2 X 106 6.62

3 1,700,000 = 1.7 X 106 6.23

4 1,400,000 = 1.4 X 106 6.15

5 400,000 = 4.0 X 105 5.60

6 1,100,000 = 1.1 X 106 6.04

7 510,000 = 5.1 X 105 5.71

Mean of log10 values = (5.78 + 6.62 + 6.23 + 6.15 + 5.60 + 6.04 + 5.71) / 7 = 6.02

Antilog of 6.02 = 1,047,128 = 1.0 x 106 geometric mean MPN of fecal coliforms / g (dry weight) 
Method 1680

29 April 2010

15.0 Sample Spiking Procedure

15.1 Method 1680 QC requirements (Section 9.0) include the preparation and analysis of spiked

reference (Milorganite®) samples in order to monitor initial and ongoing method performance. 

For the IPR (Section 9.3) and OPR (Section 9.4) analyses it is necessary to spike samples with

laboratory-prepared spiking suspensions. Section 15.0 is arranged in the following order:

preparation of the E. coli spiking suspension (Section 15.2), spiking suspension dilution (Section

15.3), spiking suspension enumeration (Section 15.4), Class A sample spiking (Section 15.5),

Class B sample spiking (Section 15.6), and calculation of spiked E. coli percent recovery (Section

15.7).

15.2 Preparation of E. coli Spiking Suspension (Class A or B)

15.2.1 Stock Culture. Prepare a stock culture by inoculating a heart infusion agar (HIA) slant

[or other non-selective media (e.g., Tryptic Soy Agar)] with Escherichia coli ATCC #

25922 and incubating at 35°C ± 3°C for 20 ± 4 hours. This stock culture may be stored

in the dark at room temperature for up to 30 days.

15.2.2 1% Lauryl Tryptose Broth (LTB). Prepare a 1% solution of LTB by combining 99 mL

of sterile phosphate buffered dilution water and 1 mL of sterile single strength lauryl

tryptose broth in a sterile screw cap bottle or re-sealable dilution water container. 

Shake to mix. 

15.2.3 Spiking Suspension (Undiluted). From the stock culture of E. coli ATCC # 25922,

transfer a small loopful of growth to the 1% LTB solution and vigorously shake a

minimum of 25 times. Incubate at 35°C ± 3°C for 20 ± 4 hours. The resulting spiking

suspension contains approximately 1.0 x 107

 to 1.0 x 108 E. coli colony forming units

(CFU) per mL. This is referred to as the “undiluted spiking suspension.”

15.3 Spiking Suspension Dilution

15.3.1 Mix the spiking suspension by vigorously shaking the bottle a minimum of 25 times. 

Use a sterile pipette to transfer 1.0 mL of the undiluted spiking suspension to 99 mL of

sterile dilution water (Section 7.4), cap, and mix by vigorously shaking the bottle a

minimum of 25 times. This is spiking suspension dilution “A.” A 1.0-mL dilution “A”

is 10-2 mL of the original undiluted spiking suspension.

15.3.2 Use a sterile pipette to transfer 11.0 mL of spiking suspension dilution “A” to 99 mL of

sterile dilution water, cap, and mix by vigorously shaking the bottle a minimum of 25

times. This is spiking suspension dilution “B.” A 1.0-mL dilution “B” is 10-3 mL of

the original undiluted spiking suspension.

15.3.3 Use a sterile pipette to transfer 11.0 mL of spiking suspension dilution “B” to 99 mL

of sterile dilution water, cap, and mix by vigorously shaking the bottle a minimum of

25 times. This is spiking suspension dilution “C.” A 1.0-mL dilution “C” is 10-4 mL of

the original undiluted spiking suspension.

15.3.4 Use a sterile pipette to transfer 11.0 mL of spiking suspension dilution “C” to 99 mL

of sterile dilution water, cap, and mix by vigorously shaking the bottle a minimum of

25 times. This is spiking suspension dilution “D.” A 1.0-mL dilution “D” is 10-5 mL

of the original undiluted spiking suspension.
Method 1680

April 2010 30

15.3.5 Use a sterile pipette to transfer 11.0 mL of spiking suspension dilution “D” to 99 mL

of sterile dilution water, cap, and mix by vigorously shaking the bottle a minimum of

25 times. This is spiking suspension dilution “E.” A 1.0-mL dilution “E” is 10-6 mL of

the original undiluted spiking suspension.

15.4 Spiking Suspension Enumeration

15.4.1 Prepare heart infusion agar (HIA) (Section 7.5), add 10 - 15 mL of HIA per 100 × 15 

mm petri dish, and allow to solidify. Ensure that agar surface is dry. Note: To ensure

that the agar surface is dry prior to use, plates should be made several days in advance

and stored inverted at room temperature or dried using a laminar-flow hood.

15.4.2 Each of the following will be conducted in triplicate, resulting in the evaluation of

nine spread plates: 

• Pipet 0.1 mL of dilution “C” onto surface of pre-dried HIA plate [10-5 mL (0.00001) of

the original spiking suspension].

• Pipet 0.1 mL of dilution “D” onto surface of pre-dried HIA plate [10-6 mL (0.000001) of

the original spiking suspension].

• Pipet 0.1 mL of dilution “E” onto surface of pre-dried HIA plate [10-7 mL (0.0000001) of

the original spiking suspension].

15.4.3 For each spread plate, using a sterile bent glass rod or spreader, distribute inoculum

over surface of medium by rotating the dish by hand or on a turntable. 

15.4.4 Allow inoculum to absorb into the medium completely.

15.4.5 Invert plates and incubate at 35°C ± 0.5°C for 24 ± 4 hours.

15.4.6 Count and record number of colonies per plate. Refer to Section 15.7 for calculation of

spiking suspension concentration.

15.5 Class A Biosolid Sample Spiking

Homogenize the unspiked Class A biosolid sample (Section 11.1). For the enumeration of fecal

coliforms in the unspiked sample, dilute and inoculate according to Section 11.2. After the

unspiked sample has been diluted and media inoculated, spike the biosolid sample as indicated

below.

Since the objective of spiking the biosolid sample is to establish percent recovery, it is necessary

to determine the number of E. coli in the undiluted spiking suspension. Instructions for spiking

suspension enumeration are provided below.

15.5.1 Liquid Samples: Since the unspiked, homogenized sample was analyzed by the

LTB/EC procedure and a dilution series was prepared (Section 11.2), 284 mL of the

original 300 mL of unspiked, homogenized sample remains. To spike the sample, add

1.0 mL of spiking suspension dilution “B” (from Section 15.3.2) for every 100-mL of

unspiked homogenized sample remaining, cover, and blend on high speed for 1 - 2

minutes. This is the “spiked, homogenized” sample. The volume (mL) of undiluted

spiking suspension added to each mL of the spiked biosolid sample is 1.0 × 10-5 mL per
Method 1680

31 April 2010

mL [(2.8 mL × 10-3 mL) / 284 mL of biosolid], which is referred to as Vspiked per unit biosolids

below. Proceed to Section 11.2.1 (dilution and inoculation).

15.5.2 Solid Samples: Since the unspiked, homogenized sample was analyzed by the LTB/EC

procedure and a dilution series was prepared (Section 11.2), 234 mL of the original 300

mL of unspiked, homogenized sample remains. To spike the sample, add 1.0 mL of

spiking suspension dilution “B” (from Section 15.3.2) for every 100-mL of unspiked

homogenized sample remaining, cover, and blend on high speed for 1 - 2 minutes. This

is the “spiked, homogenized” sample. The volume (mL) of undiluted spiking

suspension added to each g (wet weight) of the spiked biosolid sample is 1.0 × 10-4 mL

per g [(2.3 mL × 10-3 mL) / 23.4 g of biosolid], which is referred to as Vspiked per unit biosolids

below. Proceed to Section 11.2.2 (dilution and inoculation).

15.6 Class B Biosolid Sample Spiking

Homogenize the unspiked Class B biosolid sample (Section 11.1). For the enumeration of fecal

coliforms in the unspiked sample, dilute and inoculate according to Section 11.2. After the

unspiked sample has been diluted and media inoculated, spike the biosolid sample as indicated

below.

Since the objective of spiking the biosolid sample is to establish percent recovery, it is necessary

to determine the number of E. coli in the undiluted spiking suspension. Instructions for spiking

suspension enumeration are provided below.

Since a dilution series was prepared from the unspiked, homogenized sample (Section 11.2), 289

mL of the original 300 mL of unspiked, homogenized sample remains. To spike the sample, add

1.0 mL of well-mixed undiluted spiking suspension, for every 100-mL of unspiked homogenized

sample remaining after unspiked sample evaluation and dilution preparation, cover, and blend on

high speed for 1 - 2 minutes. This is the “spiked, homogenized” sample.

Note: The volumes of undiluted spiking suspensions added per mL or g (wet weight) of the

spiked Class B biosolids are different from those for the Class A biosolids, since different

volumes of the unspiked, homogenized sample remains.

15.6.1 Liquid Samples: The volume (mL) of undiluted spiking suspension added to each Ml of

the spiked biosolid sample is 1.0 × 10-2 mL [(2.9 mL spiking suspension) / 289 mL of

biosolid], which is referred to as Vspiked per unit biosolids below. Proceed to Section 11.2.3

(dilution and inoculation).

15.6.2 Solid Samples: The volume (mL) of undiluted spiking suspension added to each g (wet

weight) of the spiked biosolid sample is 1.0 × 10-1 mL per g [(2.9 mL spiking

suspension) / 28.9 g of biosolids], which is referred to as Vspiked per unit biosolids below. 

Proceed to Section 11.2.4 (dilution and inoculation).

15.7 Calculation of Spiked E. coli Percent Recovery 

Spiked E. coli percent recovery will be conducted in four steps as indicated below. Note: The

example calculated numbers provided in the tables below have been rounded at the end of each

step. If your laboratory recalculates the examples using a spreadsheet and rounds only after the

final calculation (Step 4), the percent recoveries may be slightly different.
Method 1680

April 2010 32

EC = 

CFU + 

 undiluted spike

1 + +

++ +

CFU CFU

VV V

n

n

2

1 2

...

...

15.7.1 Step 1: Calculate Concentration of E. coli (CFU / mL) in Undiluted Spiking

Suspension

15.7.1.1 The number of E. coli CFU / mL in the spiking suspension will be calculated

using all plates yielding counts within the ideal range of 30 to 300 CFU per

plate.

15.7.1.2 If the number of colonies exceeds the upper range (i.e. >300) or if the colonies

are not discrete, results should be recorded as “too numerous to count”

(TNTC).

15.7.1.3 Calculate the concentration of E. coli (CFU / mL) in the undiluted spiking

suspension according to the following equation. Example calculations are

provided in Table 8, below.

Where:

EC undiluted spike = E. coli CFU / mL in undiluted spiking suspension

CFU = number of colony forming units from HIA plates yielding counts

within the ideal range of 30 to 300 CFU per plate

V = volume of undiluted sample in each HIA plate yielding counts within

the ideal range of 30 to 300 CFU per plate

n = number of plates with counts within the ideal range of 30 to 300

CFU per plate

Table 8. Example Calculations of E. coli Spiking Suspension Concentration

Examples

CFU / plate (triplicate analyses) from 

HIA plates E. coli CFU / mL in undiluted 

spiking suspension

(EC undiluted spike) a

10-5 mL plates 10-6 mL plates 10-7 mL plates 

Example 1 275, 250, 301 30, 10, 5 0, 0, 0

(275+250+30) / (10-5+10-5+10-6) = 

555 / (2.1 x 10-5) = 26,428,571 = 

2.6 x 107

 CFU / mL

Example 2 TNTC, TNTC,

TNTC TNTC, 299, TNTC 12, 109, 32

(299+109+32) / (10-6+10-7+10-7) = 

440 / (1.2 x 10-6) =366,666,667 = 

3.7 x 108

 CFU / mL

a EC undiluted spike is calculated using all plates yielding counts within the ideal range of 30 to 300 CFU per plate
Method 1680

33 April 2010

15.7.2 Step 2: Calculate Spiked E. coli [CFU / mL or g (wet weight)]

15.7.2.1 The volume of undiluted spiking suspension per unit (mL or g) of spiked

biosolid samples (Vspiked per unit biosolids) is provided in Table 9.

Table 9. Volume of Undiluted Spiking Suspension per Unit (mL or g) of Spiked Biosolid

Samples (Vspiked per unit biosolids)

Description of spiked sample Vspiked per unit biosolids

Class A liquid 1.0 X 10-5 mL per mL of biosolids

Class A solid 1.0 x 10-4 mL per g of biosolids (wet weight) 

Class B liquid 1.0 X 10-2 mL per mL of biosolids

Class B solid 1.0 x 10-1 mL per g of biosolids (wet weight) 

15.7.2.2 Calculate concentration of spiked E. coli (wet weight) in biosolid sample

according to the following equation.

Spiked ECwet weight = (ECundiluted spike) x (Vspiked per unit biosolids)

Where:

Spiked ECwet weight = Number of spiked E. coli CFU per mL or g of biosolid

(wet weight)

ECundiluted spike = E. coli CFU / mL in undiluted spiking suspension

Vspiked per unit biosolids = mL of undiluted spiking suspension per mL or g of

spiked biosolid

Examples are provided in Table 10.

Table 10. Example Calculations of Spiked ECwet weight

EC undiluted spike V spiked Spiked ECwet weight

 2.6 x 107 CFU / mL Class A liquid: 1.0 X 10-5 mL per mL of

biosolids

(2.6 x 107 CFU / mL) x (1.0 x 10-5 mL / mL)

= 2.6 x 102

 CFU / mL

Class A solid: 1.0 x 10-4 mL per g of

biosolids (wet weight)

(2.6 x 107 CFU / mL) x (1.0 x 10-4 mL / g)

= 2.6 x 103

 CFU / g (wet weight)

Class B liquid: 1.0 x 10-2 mL per mL of

biosolids

(2.6 x 107 CFU / mL) x (1.0 x 10-2 mL / mL) 

= 2.6 x 105

 CFU / mL

Class B solid: 1.0 x 10-1 mL per g of

biosolids (wet weight)

(2.6 x 107 CFU / mL) x (1.0 x 10-1 mL / g) 

= 2.6 x 106

 CFU / g (wet weight)

3.7 x 108

 CFU / mL

Class A liquid: 1.0 X 10-5 mL per mL of

biosolids

(3.7 x 108 CFU / mL) x (1.0 x 10-5 mL / mL) 

= 3.7 x 103

 CFU / mL

Class A solid: 1.0 x 10-4 mL per g of

biosolids (wet weight)

(3.7 x 108 CFU / mL) x (1.0 x 10-4 mL / g) 

= 3.7 x 104

 CFU / g (wet weight)

Class B liquid: 1.0 x 10-2 mL per mL of

biosolids

(3.7 x 108 CFU / mL) x (1.0 x 10-2 mL / mL) 

= 3.7x 106

 CFU / mL

Class B solid: 1.0 x 10-1 mL per g of

biosolids (wet weight)

(3.7 x 108 CFU / mL) x (1.0 x 10-1 mL / g) 

= 3.7 x 107

 CFU / g (wet weight)

15.7.3 Step 3: Convert to “True” Spiked E. coli CFU / g Total Solids (dry weight)
Method 1680

April 2010 34

R

N N

T

s u = × − 100 ( )

Convert to “true” spiked CFU / g total solids (dry weight) as indicated in Section 14.3

using the E. coli mL or g (wet weight) from Section 15.7.2 as the numerator in the

equation. Examples are provided in Table 11.

Table 11. Examples of Conversion to “True” Spiked E. coli CFU / g Total Solids (Dry Weight)

Example Total Solids (CFU / mL or g) / percent total solids =True spiked E. coli CFU / g dry weight

Class A liquid: 9% 2.6 x 102

 / 0.09 = 2889 = 2.9 x 103 CFU / g dry weight

Class A solid: 82% 2.6 x 103

 / 0.82 = 3171 = 3.2 x 103 CFU / g dry weight

Class B liquid: 4% 2.6 x 105

 / 0.04 = 6,500,000 = 6.5 x 106 CFU / g dry weight

Class B solid: 23% 2.6 x 106

 / 0.23 = 11,304,348 = 1.1 x 107 CFU / g dry weight

Class A liquid: 7% 3.7 x 103

 / 0.07 = 52,857 = 5.3 x 104 CFU / g dry weight

Class A solid: 88% 3.7 x 104

 / 0.88 = 42,045 = 4.2 x 104 CFU / g dry weight

Class B liquid: 3% 3.7x 106

 / 0.03 = 123,333,333 = 1.2 x 108 CFU / g dry weight

Class B solid: 40% 3.7 x 107

 / 0.40 = 92,500,000 = 9.3 x 107 CFU / g dry weight

15.7.4 Step 4: Calculate Percent Recovery

15.7.4.1 Calculate percent recovery (R) using the following equation:

Where:

R = Percent recovery

Ns = Fecal coliform MPN/g (dry weight) in the spiked sample

Nu = Fecal coliform MPN/g (dry weight) in the unspiked sample

T = True spiked E. coli CFU /g (dry weight) in spiked sample

Example percent recovery calculations are provided in Table 12.

Table 12. Example Percent Recovery Calculations

Matrix Ns Nu T Percent recovery (R)

Class A liquid 2.5 x 103 1.5 x 101 2.9 x 103 100 x [(2.5 x 103

) - (1.5 x 101)] / 2.9 x 103 = 86%

Class A solid 3.9 x 103

 5.0 x 102 3.2 x 103 100 x [(3.9 x 103) - (5.0 x 102)] / 3.2 x 103 = 107%

Class B liquid 1.4 x 108 1.7 x 106 1.2 x 108 100 x [(1.4 x 108

) - (1.7 x 106)] / 1.2 x 108 = 115%

Class B solid 8.3 x 106 8.0 x 105 1.1 x 107 100 x [(8.3 x 106

) - (8.0 x 105)] / 1.1 x 107 = 68%
Method 1680

35 April 2010

16.0 Method Performance

16.1 Interlaboratory Validation of Method 1680

16.1.1 Twelve volunteer laboratories and a referee laboratory participated in U.S.

Environmental Protection Agency’s (EPA’s) interlaboratory validation study of EPA

Method 1680. The purposes of the study were to characterize method performance

across multiple laboratories and multiple biosolid matrices and to develop quantitative

quality control (QC) acceptance criteria. A detailed description of the study and results

are provided in the validation study report (Reference 19.2). Results submitted by

laboratories were validated using a standardized data review process to confirm that

results were generated in accordance with study-specific instructions and the October

2002 Draft version of EPA Method 1680.

16.1.2 Recovery - Method 1680 mean recoveries of fecal coliforms from Class A matrices,

compost and thermophilically digested biosolids, spiked with laboratory-prepared spikes

were 190% and 140%, respectively. Median recoveries of fecal coliforms from compost

and thermophilically digested biosolids, spiked with laboratory-prepared spikes were

130% and 120%, respectively. Mean recoveries of fecal coliforms from Class B

matrices, aerobically and anaerobically digested biosolids, spiked with laboratoryprepared spikes were 2000% and 890%, respectively. Median recoveries of fecal

coliforms from aerobically and anaerobically digested biosolids, spiked with laboratoryprepared spikes were 88% and 86%, respectively. For Milorganite® (reference matrix)

samples spiked with laboratory spiking suspensions, the mean recovery was 130%, with a

median percent recovery of 120%.

16.1.3 Precision - Method 1680 was characterized by high variability. For percent recovery, the

overall relative standard deviations (RSDs) ranged from 81% to 130% for Class A

matrices and from 170% to 360% for Class B matrices for EPA-prepared spikes. For

ambient (unspiked) fecal coliform results, the overall RSDs ranged from 22% to 250%

for Class A matrices and from 140% to 470% for Class B matrices. 

16.1.4 False positive rates - Method 1680 false positive rates were relatively low (6%) for

thermophilically digested matrices but high (32%) for the composted matrices. False

positive rates for Milorganite® could not be accurately assessed because only two

positive tubes were observed during the study. False positive rates for aerobically

digested and anaerobically digested samples were relatively low compared to Class A

rates and ranged from 5% to 10%, dependent on procedure and matrix. 

16.1.5 False negative rates - Method 1680 false negative rates for Class A matrices were

relatively low compared to Class B rates and ranged from 0% to 6%. False negative rate

for aerobically digested matrices was slightly higher (10%) compared to Class A rates. 

In contrast, the false negative rate for anaerobically digested matrices was 22%.

17.0 Pollution Prevention

17.1 The solutions and reagents used in this method pose little threat to the environment when

recycled and managed properly. 

17.2 Solutions and reagents should be prepared in volumes consistent with laboratory use to minimize

the volume of expired materials to be disposed.
Method 1680

April 2010 36

18.0 Waste Management

18.1 The laboratory is responsible for complying with all Federal, State, and local regulations

governing waste management, particularly hazardous waste identification rules and land disposal

restrictions, and for protecting the air, water, and land by minimizing and controlling all releases

from fume hoods and bench operations. Compliance with all sewage discharge permits and

regulations is also required. An overview of requirements can be found in Environmental

Management Guide for Small Laboratories (EPA 233-B-98-001).

18.2 Samples, reference materials, and equipment known or suspected to have viable bacteria or viral

contamination must be sterilized prior to disposal.

18.3 For further information on waste management, consult The Waste Management Manual for

Laboratory Personnel and Less Is Better: Laboratory Chemical Management for Waste

Reduction, both available from the American Chemical Society’s Department of Government

Relations and Science Policy, 1155 16th Street NW, Washington, DC 20036.

19.0 References

19.1 American Public Health Association, American Water Works Association, and Water

Environment Federation. 1995. Standard Methods for Water and Wastewater. 20th Edition.

Sections: 9020, 9221, 9222.

19.2 USEPA. 2004. Results of the Interlaboratory Validation of EPA Method 1680 (LTB/EC) for

Fecal Coliforms in Biosolids. EPA-821-R-04-009. December 2004.

19.3 American Chemical Society (ACS). 2000. Reagent Chemicals, American Chemical Society

Specifications. American Chemical Society, New York. For suggestions of the testing of reagents

not listed by the American Chemical Society, see AnalaR Standards for Laboratory Chemicals,

BDH, Poole, Dorset, UK and the United States Pharmacopeia.

19.4 Bordner, R., J.A. Winter, and P.V. Scarpino (eds.). 1978. Microbiological Methods for

Monitoring the Environment, Water and Wastes. EPA-600/8-78-017. Office of Research and

Development. USEPA.

19.5 Klee, A. J. 1993. A computer program for the determination of the most probable number and its

confidence limits. Journal of Microbiological Methods. 18:91-98.

20.0 Figures

The following pages include flow charts summarizing the dilution and inoculation schemes

(Section 11.0) and procedures (Section 12.0). Schemes for dilution and inoculation are

dependent on sample Class (A or B) and matrix (solid) or (liquid).
LTB/EC Method

Inoculate LTB and incubate at 

35°C ± 0.5°C for 24 ± 2 hr 

Growth and gas production No gas production

Incubate additional 24 hr 

(total of 48 ± 3 hr)

Growth and gas production

Failure to produce gas 

within 48 ± 3 hr: 

NEGATIVE fecal coliform 

Inoculate EC and incubate 

at 44.5°C ± 0.2°C 

for 24 ± 2 hr 

Growth and gas 

production within 

24 ± 2 hr: 

POSITIVE fecal coliform 

Failure to produce gas 

within 24 ± 2 hr: 

NEGATIVE fecal coliform 

FIGURE 1. MULTIPLE TUBE FERMENTATION PROCEDURE
FIGURE 2. CLASS A LIQUID SAMPLE DILUTION AND INOCULATION SCHEME 

Class A 

liquid sample

"Homogenized sample"

99 mL of sterile 

buffered dilution water

"A"

(10-1)

11.0 mL

99 mL of sterile 

buffered dilution water

"B"

(10-2)

11.0 mL

Series 1

1.0 mL of original sample 

Series 2

10-1 mL of original sample 

Series 3

10-2 mL of original sample

Delivery Volume 1.0 mL 1.0 mL 1.0 mL 

11.0 mL
FIGURE 3. CLASS A SOLID SAMPLE DILUTION AND INOCULATION SCHEME 

Class A 

solid sample

Rinse sample into blender 

with 270 mL of sterile 

buffered dilution water

"Homogenized Sample"

(10-1)

30 g

99 mL of sterile 

buffered dilution water

"A"

(10-2)

11.0 mL

99 m

buffered 

11.0 mL

Series 2

10-1 g of original sample 

Series 1

1.0 g of original sample 

in 2X medium

Series 3

10-2 g of original sample 

10.0 mL 1.0 mL Delivery Volume 1.0 mL 1
FIGURE 4. CLASS B LIQUID SAMPLE DILUTION AND INOCULATION SCHEME 

Class B 

liquid 

sample

"Homogenized sample"

99 mL of 

sterile 

buffered 

dilution 

water

"A"

(10-1)

11.0 mL

99.0 mL of 

sterile 

buffered 

dilution 

water

"B"

(10-2)

11.0 mL 11.0 mL

99.0 mL of 

sterile 

buffered 

dilution 

water

"C"

(10-3)

Series 2

10-4 mL of original sample 

Series 1

10-3 mL of original sample 

Series 3

10-5 mL of original sample

Delivery Volume 1.0 mL 1.0 mL 1.0 mL 

99.0 mL of 

sterile 

buffered 

dilution 

water

"D"

(10-4)

11.0 mL

99.0 mL o

sterile 

buffered 

dilution 

water

"E"

(10-5)

11.0 mL 
FIGURE 5. CLASS B SOLID SAMPLE DILUTION AND INOCULATION SCHEME 

Class B 

solid 

sample

30 g

99 mL of

 sterile 

buffered 

dilution 

water

"A"

(10-2)

11.0 mL 11.0 mL

99.0 mL of 

sterile 

buffered 

dilution 

water

"B"

(10-3)

Series 2

10-4 g of original sample 

Series 1

10-3 g of original sample 

Series 3

10-5 g of original sample

Delivery Volume 1.0 mL 1.0 mL 1.0 mL 

99.0 mL of 

sterile 

buffered 

dilution 

water

"C"

(10-4)

11.0 mL

99.0 mL of 

sterile 

buffered 

dilution 

water

"D"

(10-5)

11.0 mL 

Rinse sample into blender 

with 270 mL of sterile 

buffered dilution water

"Homogenized Sample"

(10-1)
Method 1680

April 2010 42

21.0 Glossary

The definitions and purposes are specific to this method but have been conformed to common

usage as much as possible.

21.1 Units of weight and measure and their abbreviations

21.1.1 Symbols:

°C degrees Celsius

< less than

> greater than

% percent

± plus or minus

21.1.2 Alphabetical characters:

EC Escherichia coli

EPA United States Environmental Protection Agency

g gram

L liter

LTB lauryl tryptose broth

mg milligram

mL milliliter

mm millimeter

MPN most probable number

NIST National Institute of Standards and Technology

QA quality assurance

QC quality control

TD to deliver

21.2 Definitions, acronyms, and abbreviations (in alphabetical order):

Analyte—The microorganism tested for by this method. The analytes in this method are fecal

coliforms.

Enrichment—A non-selective culture media for enhanced growth.

Liquid samples—Generally defined as samples containing #7% total solids (dry weight).

May—This action, activity, or procedural step is neither required nor prohibited.

May not—This action, activity, or procedural step is prohibited.

Method blank—An aliquot of sterile reagent water that is treated exactly as a sample including

exposure to all glassware, equipment, media, procedures that are used with samples. The method

blank is used to verify the sterility of equipment, materials, and supplies.
Method 1680

43 April 2010

Most probable number method (MPN)—A statistical determination of the number of bacteria per

weight or volume of sample. It is based on the fact that the greater the number of bacteria in a

sample, the more dilution is needed to reduce the density to the point at which no bacteria are left

to grow in a dilution series.

Must—This action, activity, or procedural step is required.

Negative control—A control culture that, when analyzed exactly like a field sample, will produce

a known negative result for a given type of media.

Positive control—A control culture that, when analyzed exactly like a field sample, will produce

a known positive result for a given type of media.

Preparation blank—See Method blank.

Selective media—A culture media designed to suppress the growth of unwanted microorganisms

and encourage the growth of desired ones.

Should—This action, activity, or procedural step is suggested but not required.

Solid samples—Generally, samples containing >7 % total solids (dry weight).