Public Health Inspector’s Guide To the Principles and Practices of Environmental Microbiology FEBRUARY 2013 Public Health Ontario Public Health Ontario (PHO) is a Crown corporation dedicated to protecting and promoting the health of all Ontarians and reducing inequities in health. As a hub organization, PHO links public health practitioners, frontline health workers and researchers to the best scientific intelligence and knowledge from around the world. Our mission is to support health care providers, the public health system and partner ministries in making informed decisions and taking informed action. PHO provides transparent and timely expert scientific advice, technical support and practical tools related to infection prevention and control; surveillance and epidemiology; health promotion, chronic disease and injury prevention; environmental and occupational health; health emergency preparedness; public health laboratory services; research; professional development; and knowledge services. For more information, visit www.oahpp.ca Ontario Agency for Health Protection and Promotion (Public Health Ontario). Public health inspector’s guide to the principles and practices of environmental microbiology. 4th ed. Toronto, ON: Queen’s Printer for Ontario; 2013. ISBN 978-1-4606-0678-0 [PDF] ISBN 978-1-4606-0677-3 [Print] All or part of this document may be reproduced for educational purposes only without permission. © Queen’s Printer for Ontario, 2013 Preface This revised edition of the Public Health Inspector's Guide to the Principles and Practices of Environmental Microbiology was developed by the Public Health Ontario Laboratories (PHOL) to assist Ontario’s local boards of health staff in the informed use of public health laboratory services for environmental microbiological testing. The last edition of this guide was published in 2010. This Guide is divided into several sections. It includes a contact directory for the PHOL, general information including an overview of analyses available at the PHOL, legal use of the guide, and details regarding the collection of legal samples. Subsections devoted to food, water, suspected sewage contamination, and environmental Legionella testing offer details of test menu, test requisition requirements, and collection and transportation instructions. Detailed interpretation of PHOL environmental test results is provided in table 17. This edition was made possible through extensive stakeholder participation, with distribution and engagement of all thirty six local boards of health, the Association of Supervisors of Public Health Inspectors of Ontario (ASPHIO), Canadian Institute of Public Health Inspectors (CIPHI), the Ministry of Health and Long Term Care – Public Health Policy and Programs Branch (MOHLTC-PHPPB), and the Ontario Multi-Agency Foodborne Outbreak/ Food Recall Working Group laboratory subcommittee. The success of future editions is dependant of this ongoing engagement and generosity of all who are involved in the delivery of environmental health programs and services in Ontario. This guide will be formally revised on a biannual basis. Smaller changes as tests are modified, deleted or added, will be updated in the online version. Please refer to www.oahpp.ca for the most recent edition. We welcome all suggestions and input for future editions, and look forward to ongoing collaborations with all of those involved in public health in Ontario. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y iii Note To Readers/Users The Public Health Inspector’s Guide to the Principles and Practices of Environmental Microbiology (the “Guide”) is proprietary to Public Health Ontario (“PHO” or “Ontario Agency of Health Protection and Promotion/OAHPP"). No part of the Guide shall be used, reproduced, translated, converted, adapted, stored in a retrieval system, communicated or transmitted by any means, for any commercial purpose, including without limitation, sale, resale, license, rental or lease. PHO does not make any representations, warranties or guarantees express or implied, as to the accuracy or completeness of the Guide. Users must be aware that updates and amendments will be made from time to time to the Guide. It is the responsibility of the users to determine whether there have been any such updates or amendments and PHO shall have no responsibility for providing notice of any such updates or amendments. Although the material in the Guide has been carefully prepared, neither PHO nor any of its directors, officers, employees or agents shall accept legal responsibility in any manner whatsoever for the contents and/or the improper use of this Guide. iv P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Table of Contents Contact Directory 2 General information Scope of the Guide Analyses Not Available at the PHOL Legal Use of the Guide Legal Samples – Collection Instructions 3 3 3 4 fooD samPle analysis Food – Microbiological Analysis Test Menu Food – Test Requisition Requirements Food – Collection and Transportation Instructions Food – Laboratory Rejection Criteria Environmental Swabs for Outbreak Investigations – Collection and Transportation Instructions Water samPle analysis Water – Microbiological Analysis Test Menu Water – Test Requisition Requirements Water – Collection and Transportation Instructions Drinking Water – Official Agency Submission Drinking Water – Private Citizen Submission Ice – Treated Recreational Water Facilities and Hydrotherapy Pools Public Beaches Water – Laboratory Rejection Criteria susPecteD seWaGe contamination samPle analysis Collection and Transportation Instructions LegioneLLa investiGations Legionella – Microbiological Analysis Test Menu Legionella – Selection of Sampling Sites Legionella – Environmental Sample Collection and Transportation Instructions 5 6 7 10 11 12 14 16 16 17 18 19 20 21 22 24 24 Glossary – Water terms 27 interPretation of environmental microbioloGical test results 32 ontario Public HealtH stanDarDs anD suPPortinG leGislation 36 suPPortinG Documentation/references 37 contributors 38 aPPenDices Appendix A: Supplies Appendix B: Laboratory Submission Forms A. Bacteriological Analysis of Water – Single Sample Requisition for Official Agencies B. Bacteriological Analysis of Water – Multiple Sample Requisition for Official Agencies C. Bacteriological Analysis of Drinking Water for Private Citizen, SINGLE HOUSEHOLD ONLY D. Food Bacteriology E. Environmental Bacteriology Swab Tests F. Potability of Water Release Form G. Autorisation De Divulguer Des Renseignements Sur La Potabilité De L'eau H. Ontario Agency for Health Protection and Promotion Legal Seal I.Ontario Agency for Health Protection and Promotion Regulated Water Seal Appendix C: Major Foodborne Diseases – General Features Appendix D: List of Tables 39 40 41 42 43 44 45 46 47 48 48 49 53 25 P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 1 Contact Directory customer service For inquiries, call our customer service centre at 1-877-604-4567 or 416-235-6556 between 7:30 a.m. and 7:00 p.m. or the After-hours Emergency Response Line: 416-605-3113. Visit the PHO website for more information: www.oahpp.ca PHo laboratory, toronto telephone # fax # 416-235-6556 or 1-877-604-4567 416-235-6552 81 Resources Road, Etobicoke, ON M9P 3T1 Hours of operation: toll-free Helpline: Mon. to Fri. 8:00 a.m – 5:00 p.m Mon. to Fri. 7:30 a.m – 7:00 p.m after-hours emergency response line: 416-605-3113 Key contacts: Medical Microbiologist Regional Microbiologist Manager, Enteric, Environmental, Molecular Surveillance and Sexually Transmitted Infections Head Technologist, Environmental Microbiology Environmental Microbiology - Laboratory Program Coordinator Drinking Water Testing Clinical and Environmental Microbiology Office Manager, Clinical and Environmental Microbiology PHo laboratories, reGional Hours of operation: Mon. to Fri., 8:00 a.m – 5:00 p.m after-hours emergency response line: 416-235-6063 613-547-1185 416-235-5707 416-235-5718 416-235-5716 519-455-9310 416-235-5712 416-235-5988 416-235-5951 416-235-5951 416-235-5951 519-455-3363 416-235-5951 416-235-5951 telephone # fax # 416-605-3113 Hamilton 250 Fennell Avenue West, P.O. Box 2100, Hamilton ON L8N 3R5 905-385-5379 905-385-0083 Kingston 181 Barrie Street, P.O. Box 240, Kingston ON K7L 4V8 613-548-6630 613 547-1185 519-455-9310 519-455-3363 orillia 750 Memorial Avenue, P.O. Box 600, Orillia ON L3V 6K5 705-325-7449 705-329-6001 ottawa 2380 St. Laurent Boulevard, Ottawa ON K1G 6C4 613-736-6800 613-736-6820 Peterborough 99 Hospital Drive, P.O. Box 265, Peterborough ON K9J 6Y8 705-743-6811 705-745-1257 sault ste. marie 160 McDougald Street, Sault Ste. Marie ON P6A 3A8 705-254-7132 705-945-6873 sudbury 1300 Paris Street, Suite 2, Sudbury ON P3E 6H3 705-564-6917 705-564-6918 thunder bay 336 South Syndicate Avenue, Thunder Bay ON P7E 1E3 807-622-6449 807-622-5423 timmins 67 Wilson Avenue, Timmins ON P4N 2S5 705-267-6633 705-360-2006 london St. Joseph’s Regional Mental Health Centre, 850 Highbury Avenue, 5th Floor, P.O. Box 5704, Terminal ‘A’, London ON N6A 4L6 2 416-235-5806 613-548-6630 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y General Information scoPe of tHe GuiDe: The Guide has been developed to provide Ontario's public health inspectors (PHIs) with a resource that outlines PHO Laboratories environmental microbiological testing services. This document includes information to outline the: • • • • Tests performed Specimen collection and transportation instructions Laboratory acceptance and rejection criteria Test result interpretation Environmental testing available through the PHOL includes: • Microbiological analysis of ready-to-eat foods • Environmental swab analysis for pathogen specific requests (outbreaks) • Drinking water analysis for private citizens (total Coliform and Escherichia coli only) • Drinking water analysis requested by boards of health (microbiological analysis only) • Treated ice • Recreational water facilities and hydrotherapy pools • Public beach water testing • Suspected sewage contamination samples • Environmental sampling for Legionella species • Identification of ticks removed from humans (Parasitology) Public Health Ontario Laboratories hold a drinking water testing license (Ministry of the Environment) and drinking water tests, which are limited to the scope of testing (http://www.cala.ca/cala_directories.html), are accredited by the Canadian Association for Laboratory Accreditation Inc. (CALA) to ISO 17025.The PHOL uses references and methods as guidance documents for testing from agencies such as Health Canada (HC) references, American Public Health Association (APHA) and the Association of Official Analytical Chemists (AOAC). analyses not available at tHe PHol The PHOL do not test environmental samples for the following parameters: • • • • • • • • Algal toxin testing (Blue-green algae) Chemical/ radiological analysis Foreign objects Fungal testing Live infestations Parasites and ticks from non-human sources Virus detection in food and water Giardia and Cryptosporidium in water Board of health staff are encouraged to contact the customer service centre at 1-877-604-4567 or 416-235-6556 for any further questions. Boards of health can also use other resources in the province to assist with investigations requiring these tests. Other resources available include: • Botulism Reference Service, Health Canada: (613) 957-0902 or After-hours: (613) 296-1139 • Canadian Association for Laboratory Accreditation (CALA): www.cala.ca – for a list of laboratories accredited with CALA in Ontario • Canadian Food Inspection Agency (CFIA): www.inspection.gc.ca • Ministry of Health and Long Term Care – Public Health Protection and Prevention Branch (MOHLTC-PHPPB): environmental.health@ontario.ca • Ministry of the Environment (MOE): www.ene.gov.on.ca • Ontario Ministry of Agriculture, Food, and Rural Affairs (OMAFRA): www.omafra.gov.on.ca • Standards Council of Canada (SCC): www.scc.ca – for a list of laboratories accredited with SCC in Ontario • University of Guelph Laboratory Services: www.guelphlabservices.com • Canadian Cooperative Wildlife Health Centre: www.ccwhc.ca leGal use of tHe GuiDe: The microbial analysis and acceptable limits outlined for the various parameters and sample type/source are based on current standards where available and/or guidelines based on current scientific evidence. References have been included to assist the user in obtaining further information. These guidelines are intended to serve as a general statement regarding the environmental microbiological testing services available at PHOL and are of no legal force or effect. If a local board of health is considering submitting environmental samples as part of an investigation with overlapping jurisdictions (e.g. federally or provincially inspected food plant combined with retail food outlet), and there is a discrepancy between federal and/or provincial microbial standards/acceptable limits, the local board of health should consult with its legal counsel. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 3 leGal samPles – collection instructions: According to the PHOL Quality Policy for Legal Specimens, a Legal Sample is defined as: Any laboratory specimen that has been submitted for testing to the PHOL with an intact legal seal and whose chain of custody has been maintained. Chain of custody is defined as: An unbroken documented chain of events from the time of sample collection until it is processed and completed. The PHOL must receive prior notification that a Legal Sample has been collected and will be submitted. Maintaining a proper chain of custody from collection of the sample through transport, testing and reporting ensures the integrity of the Legal Sample and that the laboratory results will stand as valid evidence in a legal case. If chain of custody is not maintained, the integrity of the Legal Sample, or the test procedures performed may be called into question, possibly rendering the laboratory results inadmissible as evidence. Therefore, it is essential to ensure that Legal Samples are handled according to proper guidelines and adhere to the following instructions: • Notify the Medical Microbiologist, Laboratory Manager or Designate in advance when Legal Samples are to be submitted (refer to the Contact Directory). • Affix and secure an official PHO and /or a law enforcement agency legal seal to the Legal Sample such that the sample cannot be opened without breaking the seal (N.B. For details on how to obtain official legal seal, please see appendix A.) The official legal seal must be initialed and dated by the individual who has affixed the legal seal. The sealed sample must be placed in an appropriate tamper evident container. • Once the Legal Sample is received in the laboratory, a Chain of Custody form must be signed by the individual delivering the samples and the legal seal verified as intact by both the individuals delivering and receiving the package. For Legal water samples, refer to Public Health Ontario’s Instructions for Official Agencies Submitting Water Samples to the Public Health Ontario Laboratories (www.oahpp.ca). 4 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Food Sample Analysis Food – Microbiological Analysis Test Menu Tables 1 to 4 provide an overview of food testing performed by the PHOL – Environmental Microbiology section, the nature of each test, and the turn around time. Turn around time is defined as the number of business days to complete testing based on date of receipt in the laboratory. This turn around time definition does not apply to tests that are onhold awaiting information to continue testing. Turn Around Time (TAT) posted in this Guide are estimates for routine tests. For some tests or at times of public health emergencies, outbreaks or exigent circumstances, turn around times may be longer than what is listed. PHO/OAHPP disclaims all warranties whether express or implied in respect of the information, including the TATs provided herein. Table 5 provides a list of food related tests which the PHOL refers to other laboratory facilities for testing. Indicator bacteria testing is performed on processed, cooked, ready-to-eat food items with the exception of heterotrophic plate count which is not performed on raw foods (e.g., fruits and vegetables) and cultured products (e.g., cheese). Pathogen specific analyses are determined based on clinical information obtained from submitters, and the food type. Provision of clinical information on the test requisition is critical in order for laboratories to provide the most appropriate testing for outbreak investigations. A final report is not issued until all tests for a submission are complete. table 1: indicator bacteria test nature of test turn arounD time Heterotrophic Plate Count Bacterial culture 2 days Total Coliform Count Bacterial culture 2 days Escherichia coli Count Bacterial culture 3 - 5 days Total Gram Negative Count Bacterial culture 1 day table 2: foodborne Pathogens nature of test turn arounD time Bacillus cereus test Bacterial culture 2 – 4 days Campylobacter jejuni Bacterial culture 4 – 6 days Clostridium perfringens Bacterial culture 1 – 5 days Escherichia coli O157:H7 Bacterial culture 2 – 9 days Listeria monocytogenes Bacterial culture 4 – 8 days Salmonella species Bacterial culture 4 – 6 days Shigella species (not routinely performed) Bacterial culture 2 – 6 days Staphylococcus aureus Bacterial culture Detection of bacterial toxins 2 – 4 days 2 days Vibrio species Bacterial culture 2 – 7 days Yersinia enterocolitica Bacterial culture 12 – 14 days nature of test turn arounD time pH Hydrogen ion measurement with ion selective electrode 1 day Phosphatase Measurement of alkaline phosphatase in dairy products by fluorometric assay 1 - 2 days Water Activity – aw Measurement of unbound water in food by chilled-mirror dewpoint technique 1 day table 3: Physiochemical tests test P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 5 table 4: molecular typing test Pulsed field gel electrophoresis (PFGE) nature of test turn arounD time Molecular typing 3 – 5 days table 5: referred tests test referral laboratory Clostridium botulinum Testing performed at: Botulism Reference Service Health Canada Room D457, Sir Frederick G. Banting Building, Building 22, Tunney’s Pasture, PL2204E 251 Sir Frederick Banting Driveway Ottawa, ON K1A 0K9 Telephone: (613) 957-0902 Cryptosporidium Cyclospora Giardia Hepatitis A Norovirus Prion disease Toxoplasma Trichinella The tests listed may be referred to other testing facilities. Please contact the Toronto PHOL Environmental Laboratory at 416.235.5716. Food – Test Requisition Requirements The PHOL Food Bacteriology requisition (see Appendix B) must be used to submit foods to the PHOL for analysis. It is important to provide as much of the information requested. submitter iDentification Information required includes the local board of health office address and the name, phone and fax number of the PHI or other staff submitting the samples. outbreaK number An outbreak number should be assigned for all outbreak related specimens. In some cases, the outbreak number is the only way the laboratory can correlate results from multiple submissions of foods and other related specimens from a single outbreak. PurPose of collection: (Mark the appropriate box) • Routine surveillance: Regular, on-going sanitary monitoring programs of food prepared/served in retail food establishments. Samples collected in the absence of foodborne disease. • HaccP (Hazard analysis critical control Point): Food collected in association with evaluating or monitoring critical control points in food preparation, production and processing. 6 • special survey: Special investigations of specific food items conducted by local boards of health. Surveys are usually negotiated with the laboratory prior to collection and analysis may be altered to accommodate a specific need. • complaint samples: Samples submitted for laboratory evaluation associated with the investigation of foodborne illness. Complaints usually come from the general public to the local board of health office. fooDborne illness: (Mark the appropriate box) • Part of meal: Foods submitted in conjunction with a suspect foodborne illness incident which are part of the actual meal implicated in the outbreak. • control samples: Foods submitted in conjunction with a suspected foodborne illness incident which were not part of the suspect meal, but which are of the same type and/or prepared and stored under similar conditions as those actually consumed. • follow-up samples: Samples taken after remedial action to determine whether or not the problem has been resolved. P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y ePiDemioloGical information: • Provide the predominant symptoms of illness in the space provided. • Provide the time and date of onset of symptoms. • Provide the confirmed or suspected etiological agent (if suspect indicate as such on requisition). • Provide the time and date the suspect meal was consumed. • Provide the location(s) the suspect meal was prepared and consumed. samPle DescriPtion/iDentification: • Samples must be identified by their common name on the requisition in the column labeled Sample Description (e.g. “Roast Beef”). • In addition, a unique identifier must be present on the sample bag and on the requisition under the column labeled Sender’s Number. The number must uniquely identify the food submission to assist tracking of samples during outbreaks and is designated at the discretion of the submitter. Duplication of numbers should be avoided to prevent mismatching of samples. • The marking must be sufficiently unique that the sample cannot be confused with other similar samples in the laboratory. • Detailed information will facilitate food recalls should a product be contaminated. The following information should be collected when available (a photo or photocopy of the product label would facilitate this data gathering process): o o o o o o o o o o o o o o o Brand name Common name Unit size (e.g. 50g or 125 mL, etc.) Lot number(s) Dates: Best before/Expiry/Use by/Durable life/ Packed on/Manufacturing Location of purchase Universal product code (UPC) Name of Manufacturer/Importer/Legal Agent (if available on the packaging) Label claims/preparation or serving instructions Container type (e.g. vacuum pack, plastic rigid container, etc.) Shelf life of product (if possible) Where the sample was taken (e.g. at the suspect place of eating or the case's home) Storage information (e.g. frozen, refrigerated, nonrefrigerated etc.) Indicate if this is an opened or unopened sample Indicate the number of samples/sub-samples taken Food – Collection and Transportation Instructions Table 6 provides information and sampling instructions for food. table 6: food – collection and transportation instructions Epidemiological and Risk Based Prioritization of Food Sample Collection in Foodborne Outbreaks1 instructions Precautions Selection of food items for collection and submission in a foodborne outbreak should be based on all available epidemiological and laboratory information related to the outbreak. • Epidemiological analyses, such as the calculation of attack rate, will facilitate prioritization of those food items that are most likely to be involved. • If attack rates are unavailable, incubation period, clinical syndrome and basic demographic information about related cases should be used. The integration of information about the clinical pathogen, if known, should also facilitate prioritization of food items to be collected and tested. Pathogen specific high risk foods are presented in Appendix C. • If risk stratification of food sources is not performed by the submitting public health inspector, and there is an abundance of specimens submitted for testing, prioritization will be determined by the head technologist and medical microbiologist of the PHOL Environmental Microbiology section. • The communication of all available clinical, epidemiological microbiological information to the PHOL is of great importance in guiding these decisions. For full details please consult Foodborne disease outbreaks : guidelines for investigation and control. World Health Organization 2008. http://whqlibdoc.who.int/publications/2008/9789241547222_eng.pdf Accessed February 14, 2010. 1 P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 7 table 6: food – collection and transportation instructions ...continued Containers for Sampling and Submission of Foods instructions Precautions Sterile plastic sample bags with round wire closure are the preferred sample container for all food types. Food samples found in the original container can be submitted in the original packaging provided that the container is air-tight and will not leak during transit. • If sampling closed or intact samples, please consult with the CFIA prior to submission. If the original container has been opened or if the packaging is fragile and may be damaged during transit, samples should be transferred from the original container to a sterile plastic sample bag with round wire closure. • Styrofoam and box-board packaging used for fast-food products are examples of containers that are not suitable for bacteriological sampling. They are not air tight and may leak causing cross contamination of samples and/ or external contamination into the sample. • These containers should not be put inside a sterile sample bag with round wire closure since the outside surfaces will be contaminated by handling and the sample may be compromised in transit. Preparation As part of good aseptic technique, the time taken for the physical collection of the sample can be minimized by ensuring the following: instructions Precautions Ensure all materials required are available. Label sample bags before sample collection. Investigate before sampling to determine plan of action that will minimize sampling time. Complete requisition(s) before or after, never during, sample collection. Collection of Sample(s) Precautions instructions Use aseptic technique at all stages of sample collection. • Failure to do so will compromise the laboratory results. Collect samples that are representative of each item of food that is being investigated. • Submit a minimum of 200 grams of each sample if possible as multiple tests may be required. Meals that contain multiple discreet items may be collected individually or combined for submission. • Separation of meals or mixed foods must be performed at the sampling stage. The laboratory will not separate components of a sample received in the laboratory. • If an individual component is of greater interest than other components of a meal or mixed food, sample the items individually and they will be tested as individual samples. • If collected as a single sample, components should be collected in approximately equal amounts and will be tested as one sample. Foods that contain multiple items (e.g. meat and gravy, sandwiches) may be collected as a single sample. The mouths of sterile plastic sample bags with round wire closures should be rolled down several times and the wire ends twisted together tightly to ensure and prevent leaking during transport. 8 • Leaking samples will be rejected by the laboratory. P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table 6: food – collection and transportation instructions ...continued Large Lots of Food Most commercially prepared foods are produced in very large lots. instructions Where possible, mix the lot of food before sampling. Precautions • If you encounter a lot of food that is larger than 2 kilograms, take five sub-samples of 200 grams each and submit for individual analysis. • Ensure sub-samples are clearly and distinctly labeled with a unique identifier for tracking. Small Quantity Samples Situations may be encountered where there is very little sample left. instructions In food poisoning cases, small samples will be processed by the laboratory, but complete analysis may not be possible. Precautions • If you suspect, or have a confirmed etiological agent, indicate the information on the requisition form and the specific analysis will be given priority. • In the absence of such information, the laboratory will exercise judgment and will perform analyses that will most likely provide useful information. Sample Storage instructions Precautions It is preferable to deliver samples to the laboratory as soon as possible after collection. • If there is a delay, samples must be stored in a secure location where they cannot be tampered with or confused with other food. Shelf stable foods should be stored in a dry location protected from light and extreme temperatures. • Temperatures outside 15°C to 30°C may compromise the sample(s) and impact the quality of laboratory results. Frozen foods should be stored as close to the temperature at which they were found as possible. • Temperatures above freezing may result in thawing and impact the quality of laboratory results. Perishable foods should be stored at 2 to 4°C. • Temperatures outside of this range may impact the quality of laboratory results. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 9 table 6: food – collection and transportation instructions ...continued Shipping Containers instructions Precautions Ship all foods in containers with hard walls and lids secured in the closed position. Shipping containers must be labeled with the submitting organization, unique identifier and contents e.g. FOOD SAMPLES on the outside of the container. Shipping containers used for food samples should be dedicated to food samples and not be used for other types of environmental samples. • Samples must be made secure inside the shipping container so that there is no physical damage to the samples that may cause leakage. • Shipping containers should be decontaminated between uses with an appropriate disinfectant and used according to the manufacturer’s instructions. Ship dry foods and other shelf stable foods at ambient temperature in a closed container. • Temperatures outside 15°C to 30°C may compromise the sample(s) and impact the quality of laboratory results. Ship frozen foods to the laboratory in an insulated container with sufficient ice packs to maintain the frozen state. • Temperatures above freezing may result in thawing and impact the quality of laboratory results. Ship perishable foods in insulated containers with sufficient cold packs to maintain a temperature as close to 4°C as possible. If ice is used, contain the ice in a manner that does not allow water contact with the samples. • Temperatures outside of this range may impact the quality of laboratory results. Transit Time instructions Precautions Submit food samples to the laboratory as soon as possible or within 48 hours. Samples collected during foodborne disease investigations that are part of the implicated meal will not be rejected after 48 hours. These samples are often the only opportunity to determine the cause of an outbreak. • Shipping time must be taken into consideration when transporting samples. • Routine Surveillance /HACCP samples older than 48 hours will be rejected. • Transit time needs to be considered in result interpretation as prolonged transit time may compromise test results. Food – Laboratory Rejection Criteria Table 7 outlines the various reasons a food sample will be rejected by the PHOL. If rejected, a new sample must be submitted with a completed requisition. table 7: food – laboratory rejection criteria DescriPtion 10 reason for rejection Sample Type • Specimen received from an unauthorized submitter e.g. private citizen, or no board of health identifier Sample Requisition • Requisition received with incomplete information e.g. unique identifiers missing from requisition, sample collection bag or both • Requisition received separated from the sample collection bag with no unique identifier to link them Sample Collection • Inappropriate sampling container • Raw foods requiring processing or cooking before consumption unless linked to a specific outbreak and discussed with the medical microbiologist prior to submission • Insufficient amount of sample submitted Sample Transport •Sample leaked in transit • Sample received with evidence of temperature abuse in transit P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Environmental Swabs for Foodborne Outbreak Investigations – Collection and Transportation Instructions Table 8 provides sampling instructions for environmental swabs. These instructions are limited to the use of swabs during foodborne outbreak investigation. Environmental swabs may be processed during foodborne outbreak investigations for the presence or absence of a specified bacterial pathogen from a physical environment (e.g. cutting board, meat slicer etc.). These are available (for outbreaks and foodborne illness(es) investigation only) from the Toronto Public Health Laboratory at 416-235-5716. The environmental swabs available from the PHOL contain neutralizing solution as transport medium. This medium can neutralize the following sanitizers: iodophores including chlorine compounds, quaternary ammonium compounds and phenolic sanitizers. table 8: sampling instruction for environmental swabs in foodborne outbreak investigations samPlinG instructions Precautions 1. Open the sterile swab container, grasp the handle end of the swab being careful not to touch any portion that might be inserted into the vial, and remove the swab aseptically. 2. Moisten the swab head and press out the excess solution against the interior wall of the vial with a rotating motion. 3. Hold the swab handle to make a 30° angle contact with the surface. Rub the swab head slowly and thoroughly over approximately 50 cm2 of the surface three times, reversing direction between strokes. • If the sample area is large, multiple sections may be swabbed with one swab. • For an investigation where sampling areas are smaller and physically different, a new swab should be used for each section. 4. After the area has been swabbed, using aseptic technique, return the swab to the vial. • Ensure the vial is closed tightly to prevent leakage and specimen rejection. 5. Complete all sections of the Environmental Bacteriology Swab Tests requisition (see Appendix B) with appropriate information to ensure accurate tracking of the sampling. 6. Swabs should be stored and transported to the lab at 2 to 6°C and optimally tested within 24 hours of collection. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 11 Water Sample Analysis Water – Microbiological Analysis Test Menu The Health Protection and Promotion Act, section 41 (4) provides public health inspectors and medical officers of health the ability to make, take and remove or require the making, taking and removal of copies, samples or extracts related to an examination, investigation, test or inquiry. Sampling of drinking water may be required as part of an outbreak investigation, a response to a report of a health hazard or part of a routine inspection to ensure drinking water is potable. Boards of health staff are discouraged from collecting routine samples from regulated drinking water systems as this testing is performed by accredited and licensed commercial laboratories on a regular basis. All drinking water must be tested within 48 hours of collection while non potable samples are tested within one calendar day of collection. Samples should be kept cool and delivered to the laboratory as soon as possible. For samples requiring analysis for a bacteriological healthrelated parameter not included in Ontario Drinking Water Quality Standards (Ontario Regulation 169/03) e.g. Heterotrophic Plate Count (HPC) or Background, and submitted under a Provincial Officer’s Order or Certificate of Approval from a regulated drinking water system, please contact the Program Coordinator Drinking Water Testing for more information (refer to the Contact Directory). 12 If boards of health personnel wish to engage in a study involving drinking water (e.g. to identify trends associated with ground water contamination in various geographic areas, etc.), the Program Coordinator, Drinking Water Testing must be notified prior to sampling. Refer to section 5 of O. Reg 248/03 Drinking Water Testing Services regulation for specific requirements associated with drinking water research. Table 9 provides an overview of water testing performed at the PHOL for various types of water samples. The table also identifies the type of sample container required for submission and the laboratory turn around time (TAT) for each test performed. Turn around time is defined as the number of business days to complete testing based on date of receipt in the laboratory. This turn around time definition does not apply to tests that are on-hold awaiting information to continue testing. Turn Around Times posted in this Guide are estimates for routine tests. For some tests or at times of public health emergencies, outbreaks or exigent circumstances, turn around times may be longer than what is listed. PHO/OAHPP disclaims all warranties whether express or implied in respect of the information, including the TATs provided herein. P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table 9: Water – microbiological analysis test menu samPle DescriPtion samPle container tests PerformeD turn arounD time Bottled Water * PHOL water sample bottle – 200mL Total coliform Escherichia coli Pseudomonas aeruginosa Staphylococcus aureus Heterotrophic plate count 2 – 4 days 2 – 4 days 2 – 5 days 2 – 6 days 2 – 5 days Ice – Treated Sterile plastic bag with round wire closure Total coliform Escherichia coli Heterotrophic plate count (HPC performed on request for treated water only) 2 – 4 days 2 – 4 days 2 – 5 days Official Agency - Drinking Water Analysis ** PHOL water sample bottle – 200mL Total coliform Escherichia coli Heterotrophic plate count (HPC performed on request for treated water only) 2 – 4 days 2 – 4 days 2 – 5 days Outbreak samples *** Dependent on type of analysis required (Contact the PHOL, Toronto for more information) Dependent on type of analysis required (Contact the PHOL, Toronto for more information) Dependent on type of analysis required (Contact the PHOL, Toronto for more information) Private Citizen – Drinking Water Analysis PHOL water sample bottle – 200mL Total coliform Escherichia coli 2 – 4 days 2 – 4 days Public Beaches PHOL water sample bottle – 200mL Escherichia coli 2 – 4 days Recreational Water Facilities and Hydrotherapy Pools PHOL water sample bottle – 200mL Total coliform Escherichia coli Pseudomonas aeruginosa Staphylococcus aureus Heterotrophic plate count 2 – 4 days 2 – 4 days 2 – 5 days 2 – 6 days 2 – 5 days Specific Etiological Agents Refer to Table 10 Dependent on type of analysis required (Contact the PHOL, Toronto for more information) Dependent on type of analysis required (Contact the PHOL, Toronto for more information) Dependent on type of analysis required (Contact the PHOL, Toronto for more information) Suspected Sewage Contamination PHOL water sample bottle – 200mL Escherichia coli 2 – 4 days NOTES: * Commercial sealed products are not accepted. Contact the Canadian Food Inspection Agency if analysis of a sealed product is required. ** For samples submitted under an Ontario drinking water regulation, laboratories have an obligation to report test results as outlined in section 18 of the Safe Drinking Water Act, 2002. The accompanying requisition must have all required information completed prior to receipt at the laboratory or the sample will not be tested and a new sample and completed requisition submitted. *** A Public Health Inspector or designate under the authority of the Medical Officer of Health may collect water samples from drinking water systems under the Ontario drinking water regulations if required for investigational purposes in outbreak situations. These samples must be identified as “Non-Regulated” with “Outbreak Investigation” identified on the requisition. These samples are not governed by the Safe Drinking Water Act requirements. The Ontario Drinking Water Quality Standards do not apply and there is no requirement for testing to be performed by a licensed / accredited method. PHOL reporting requirements apply. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 13 Table 10 provides a list of additional analyses which may be performed in outbreak situations or upon special request. These MUST be submitted as NON-REGULATED requests only. table 10: Water – microbiological analysis test menu – Pathogen specific analyses samPle container tests PerformeD turn arounD time Campylobacter species PHOL water sample bottle – 200mL Bacterial culture 4 – 6 days Escherichia coli O157:H7 PHOL water sample bottle – 200mL Bacterial culture 2 – 9 days Legionella species PHOL water sample bottle – 200mL Potable – 1000mL (5X200mL) Non-potable – 200mL Bacterial culture 10 – 15 days Pseudomonas aeruginosa PHOL water sample bottle – 200mL Bacterial culture 2 – 5 days Salmonella species PHOL water sample bottle – 200mL Bacterial culture 4 – 6 days Staphylococcus aureus PHOL water sample bottle – 200mL Bacterial culture 2 – 6 days Vibrio cholerae PHOL water sample bottle – 200mL Bacterial culture 2 – 7 days Yersinia species PHOL water sample bottle – 200mL Bacterial culture 12 – 14 days analysis Water – Test Requisition Requirements Table 11 provides direction on the completion of the Official Agency “Bacteriological Analysis of Water – Single Sample” and “Bacteriological Analysis of Water – Multiple Sample” requisitions. For detailed instructions related to the completion of these forms and reporting requirements, refer to Public Health Ontario’s Instructions For Official Agencies Submitting Water Samples to the Public Health Ontario Laboratories (http://www.oahpp.ca/services/watertesting.html). When submitting samples for analysis to the PHO Laboratories it is important that all samples submitted under O.Reg.319/08 and O.Reg.170/03 are properly identified so that the appropriate reporting and licensing requirements can be met. For general information refer to the Ministry of Environment’s “Practices for the Collection & Handling Of Drinking-Water Samples” (April 1, 2009 or as current) http://www.ene.gov.on.ca/publications/4464e01.pdf table 11: Water – test requisition requirements Non Potable Water samPle tyPe samPle information – non - Potable (tick off) rePortinG / testinG requirements comments Public beach Public beach - PHO Reporting Requirements Public pools, spas, wading pools, splash pads/spray pads, or water slide receiving basins Recreational water facility / hydrotherapy pool - PHO Reporting Requirements Water suspected of being contaminated with fecal material Suspected sewage contamination - PHO Reporting Requirements Samples must be submitted in a Sewage Sample Collection Kit Other non potable sources Other - PHO Reporting Requirements Indicate the source PHo = Public Health Ontario 14 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table 11: Water – test requisition requirements ...continued Potable Water samPle tyPe tyPe of DrinKinG Water systems (tick off) reason for samPlinG (tick off) source of DrinKinG Water (tick off) aPPlicable reGulations anD rePortinG / testinG requirements comments Bottled water Non Regulated Applicable tick box(es) Bottled Water - PHO Reporting Requirements Commercial sealed products are not accepted (contact CFIA) Drinking water system O. Reg 170 / 03 under the SDWA SDWA O. Reg 170/03 Applicable tick box(es) Applicable tick box(es) - O. Reg 170 / 03 and O. Reg. 169/03 under the SDWA - O. Reg. 170/03 (upload exempt) - ODWQS apply - Licensed / accredited methods - All required fields of the form must be completed - Unbroken chain of custody required: Use Regulated Water Seal or complete “Relinquished By” section on form Drinking water system O. Reg 319 / 08 under the HPPA HPPA O. Reg 319/08 Applicable tick box(es) Applicable tick box(es) - O. Reg 319 / 08 under the HPPA - O. Reg. 169/03 under the SDWA - O. Reg. 319/08 (including upload to LRMA) - ODWQS apply - Licensed / accredited methods - All required fields of the form must be completed - Unbroken chain of custody required: Use Regulated Water Seal or complete “Relinquished By” section on form Drinking water systems that fall outside Ontario drinking water regulations HPPA Regulated Premises Or Non Regulated Applicable tick box(es) Applicable tick box(es) - O. Reg. 169/03 under the SDWA - PHO Reporting Requirements - ODWQS apply - Licensed / accredited methods Refer to Table A in “Glossary Water Terms” for definitions and examples Ice Non Regulated Applicable tick box(es) Other and indicate “Ice” and any applicable tick box(es) - PHO Reporting Requirements Treated ice only Other potable water sources Non Regulated Applicable tick box(es) Other - PHO Reporting Requirements Indicate the source Private well Private Residence Applicable tick box(es) Applicable tick box(es) - O. Reg. 169/03 under the SDWA - PHO Reporting Requirements - ODWQS apply - Licensed / accredited methods HPPa = Health Protection and Promotion Act oDWqs = Ontario Drinking Water Quality Standards PHo = Public Health Ontario sDWa = Safe Drinking Water Act, 2002 P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 15 Water – Collection and Transportation Instructions Table 12 provides information and sampling instructions for drinking water (both official agency and private citizens); ice (treated); recreational water facilities and hydrotherapy pools and public beaches. table 12: Water – collection and transportation instructions Drinking Water – Official Agency Submissions The PHOL tests drinking water samples for the microbiological indicators total coliforms and Escherichia coli. A heterotrophic plate count (HPC) may be requested on a distribution system sample or other treated water if necessary. Refer to the Ministry of Health and LongTerm Care Drinking Water Protocol 2008 (or as current) for more information about drinking water protocols. samPlinG instructions Precautions 1. Complete the required information on the requisition. The sample will not be tested if all of the required information is not complete or accurate when received at the laboratory, and a new sample and completed form will be required to be submitted. 2. Remove any aerator, screen or other attachment(s) from the faucet. Alternatively, take a sample from an inside tap with no aerator. Do not take a sample from an outside faucet or the garden hose. 3. Disinfect the end of the faucet spout with an alcohol swab, or diluted bleach solution (1 part household bleach to 10 parts water), before running water to remove debris or bacteria. Disinfecting the tap with a flame is not recommended because this can damage faucets. 4. Turn on cold water and let it run for 2-3 minutes to remove standing water from the plumbing system. 5. Wash hands with soap and water and dry them thoroughly prior to taking the sample. 16 6. Examine the lid of the PHOL collection bottle. If the tamper evident ring has separated from the cap use another collection bottle. 7. Remove one of the barcodes on the bottle and apply it to the top copy of the requisition in the “Barcode” field. Samples will not be processed if the barcode is not affixed to the top copy of the requisition. If the barcode is not able to be removed, write the barcode number on the form. 8. Remove the sample bottle lid. • Do not touch the inside of the lid • Do not put the lid down • Do not rinse out the bottle as this will remove the sodium thiosulfate which neutralizes the chlorine residual before testing in order to maintain bacterial viability during sample transport to the laboratory. • Do not ingest; for accidental exposure get medical attention. 9. Fill bottle to the 200mL fill line. Close the lid firmly. If overfilled, pour excess water out so there is just 200mL of water in the bottle. 10.Refrigerate the water sample or keep it in a cooler with frozen ice packs if it can not be delivered to the laboratory within six (6) hours. • Do not freeze the sample. • Samples received at the laboratory above 25°C will not be tested. 11.Keep the water sample cool (but not frozen) until it is delivered to the drop-off location. All drinking water must be tested within 48 hours of collection for the results to be suitable for the purposes of the Safe Drinking Water Act, 2002. P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table 12: Water – collection and transportation instructions ...continued Drinking Water – Private Citizen Submission The PHOL tests Private Citizen drinking water from a “single household” for the microbiological indicators total coliforms and Escherichia coli. The information below outlines the requirements for submitting private citizen drinking water samples for testing by non official agency clients. Private Citizens are required to use the PHO collection kit which includes a Bacteriological Analysis of Drinking Water for Private Citizen, SINGLE HOUSEHOLD ONLY requisition and barcoded collection bottle when submitting samples for testing. For more information refer to the Water Testing Information page at http://www.oahpp.ca/services/water-testing.html. samPlinG instructions Precautions 1. Remove screen or other attachment(s) from tap. 2. Disinfect the end of the faucet with an alcohol swab or dilute bleach solution (1 part household bleach to 10 parts water). 3. Run the cold tap for 2 - 3 minutes before collecting sample. 4. Fill the PHO Public Health Laboratory water collection bottle to the 200 mL fill-line (Maximum amount) and recap bottle immediately. • Do not rinse the bottle before filling. It contains a preservative (i.e. 0.8mM Sodium Thiosulphate. Do not ingest. For accidental exposure get medical attention). • Do not touch inner surface of cap or bottle with anything other than the water collected. 5. Keep the sample cold (e.g. refrigerated and do not freeze). Bring it to the drop off location as soon as possible in a cooler with frozen ice packs. • Ensure the form is completely and accurately filled in. Samples will not be tested if the form is not complete when received at the laboratory, and a new sample and completed form will be required to be submitted. • Results are unreliable if the sample is improperly collected, stored or transported. • Samples received at the laboratory above 25°C will not be tested. • All drinking water must be tested within 48 hours of collection for the results to be suitable for the purposes of the Safe Drinking Water Act, 2002. 6. In most cases, samples are transported from the drop off location (e.g. the local board of health office) by courier to the PHO Public Health Laboratory For laboratory locations refer to www.oahpp.ca. For local board of health locations refer to http://www.health.gov.on.ca/ important information regarding Private citizen submissions: requisition • The “Bacteriological Analysis of Drinking Water for Private Citizen, SINGLE HOUSEHOLD ONLY” form is not to be used for drinking water from a drinking water source under one of Ontario’s drinking water regulations. Owner / operators of these systems must use licensed and accredited commercial laboratories for their routine testing. • The form must be complete and accurate upon receipt at the PHOL or the sample will not be tested and another sample with another completed form submitted. • The PHOL will not release results to Private Citizen clients by fax or over the telephone. sample • Private Citizens wishing to submit water they use for drinking from surface water sources such as lakes, rivers or streams should be advised not to submit them unless the water has been properly treated first. • Three consecutive samples, taken 1 to 3 weeks apart, are needed to determine the stability of the water supply. If the well shows acceptable total coliform / E. coli counts, then sample three times a year. • Samples are analyzed for the indicators of bacterial contamination total coliform and E.coli. Samples are not tested for other contaminants, including chemical contaminants, and therefore may be unsafe to drink even when there is no significant evidence of bacterial contamination. Clients are directed to consult their local board of health for information on testing for other contaminants. • If technical difficulties should arise, it may be necessary to refer samples to another licensed laboratory within the PHOL system. Submission of a drinking water sample with the test requisition grants consent to the transfer of the sample if necessary. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 17 results • Submitters are to indicate on the form how they wish to receive their report: a) By mail b) Picked up at the laboratory if indicated on the requisition. Photo identification is required when picking up the report. Anyone wishing to pick up the report on behalf of the submitter must have a Potability of Water Release form signed by the submitter, and show photo ID when picking up the report. Refer to Appendix B or http://www.oahpp.ca/services/water-testing.html. Alternately, a Freedom of Information request may be submitted to the PHO Privacy Officer (refer to www.oahpp.ca). c) By Interactive Voice Response (IVR). The sample results and interpretation are available by calling 1-877-723-3426 and keying in the barcode associated with the sample. Teletypewriter (TTY): 1-866-828-2238. • Private Citizen clients requiring assistance with the interpretation of results or advice on the correct course of action are to contact their local board of health. table 12: Water – collection and transportation instructions ...continued Ice – Treated The PHOL tests treated ice samples for the microbiological indicators total coliforms and Escherichia coli and Heterotrophic Plate Count. samPlinG instructions Precautions 1. Complete the required information on the requisition and label sample bag(s) with unique identifier that matches that on the requisition. Ensure all materials required for sample collection are available prior to collection – sterile plastic sample bags with round wire closure, test requisition, sterile collection device (if required). 2. Wash hands with soap and water and dry them thoroughly prior to taking the sample. 3. Collect representative ice samples using either the collection device located in the freezer unit or another sterile collection device. Use aseptic technique at all stages of sample collection. Failure to do so may compromise the laboratory results. 4. Ensure the sample bag is properly secured to prevent sample leakage. 5 Transport sample(s) and accompanying requisition to the laboratory with a freezer pack in the appropriate transport container. 18 Samples must be received in the laboratory within 48 hours of collection. P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table 12: Water – collection and transportation instructions ...continued Recreational Water Facilities and Hydrotherapy Pools The PHOL tests recreational water facilities and hydrotherapy pool samples for the microbiological indicators total coliforms, Escherichia coli, Pseudomonas aeruginosa, Staphylococcus aureus and Heterotrophic Plate Count. Refer to the Ministry of Health and Long-Term Care Recreational Water Protocol 2008 (or as current) for more information about recreational water facilities and hydrotherapy pools protocols. Microbiological sampling may be conducted to evaluate and monitor cleaning and sanitizing procedures and to ensure that a health hazard does not exist. Note: for hydrotherapy pools/baths, samples are to be obtained from a sanitized tub after fresh water has circulated for a minimum of two minutes. samPlinG instructions Precautions 1. Complete the required information on the requisition. 2. Examine the lid of the PHOL collection bottle If the tamper evident ring has separated from the cap use another bottle. 3. Remove one of the barcodes on the bottle and apply it to the top copy of the requisition in the “Barcode” field. Samples will not be processed if the barcode is not affixed to the requisition. If the barcode is not able to be removed, write the barcode number on the form. 4. Hold the bottom of the PHOL sample bottle and aseptically remove the cap. • Do not touch the inside of the lid • Do not put the lid down • Do not rinse out the bottle as this will remove the sodium thiosulfate which neutralizes the chlorine/bromine residual before testing in order to maintain bacterial viability during sample transport to the laboratory. • Do not ingest; for accidental exposure get medical attention. 5. Plunge the bottle, neck downward, at a 45 degree angle to 30 cm below the water surface. Fill the bottle at that depth with a sweeping forward motion ahead of the hand, bringing the bottle up toward the water’s surface. • Take samples in an appropriate location of the pool in order to provide an accurate representation of the water in the pool. • Keep the bottle away from your other hand and body parts. • Avoid contamination from floating debris. 6. If necessary, discard some water so that the bottle is only filled with water to the 200 mL fill line indicated on the bottle. Carefully put the cap back on the bottle. 7. Transport sample(s) to the laboratory with a frozen freezer pack in the appropriate transport container as soon as possible after sample collection. • DO NOT freeze the sample. • Samples must be received in the laboratory within one calendar day of collection. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 19 table 12: Water – collection and transportation instructions ...continued Public Beaches The PHOL tests public beach water samples for the microbiological indicator Escherichia coli. Refer to the Ministry of Health and Long-Term Care Beach Management Protocol, 2008 (or as current) for more information about the protocol for public beaches. Prior to the beginning of each beach season, notify the PHOL of the number of samples that will be submitted, day(s) of week for sampling, and approximate time of day that samples will arrive at the laboratory. Note: Collect five (5) samples at designated sites at each identified beach location. More than five (5) samples may be required for larger beaches. samPlinG instructions Precautions 1. Complete the required information on the requisition. 2. Remove one barcode from the bottle and apply it to the top copy of the requisition in the “Barcode” field. Samples will not be processed if the barcode is not affixed to the requisition. If the barcode is not able to be removed, write the barcode number on the form. 3. Examine the lid of the bottle. If the tamper evident ring has separated from the cap use another bottle. 4. Remove cap and ensure it is kept away from sources of contamination. • Do not touch the inside of the lid • Do not put the lid down 5. Plunge bottle downward into water to 30 cm – turn bottle in direction point of current. • Where the depth of water is 1 to 1.5 meters, the samples are to be obtained at 15 to 30 cm below the water surface. • Where the depth of water is less than one (1) meter, obtain samples as far off shore as possible, but within swimming area. 6. Remove bottle from water. If the bottle is filled to the top, remove some of the water so it is filled to 200mL line. 7. Replace cap. 8. Store and transport samples below between 1°C and 10°C (preferably 4°C) within one calendar day of collection. 20 • DO NOT freeze the sample. • Samples must be received at the laboratory within one calendar day after collection. P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Water - Laboratory Rejection Criteria Table 13 outlines the various reasons a water sample will be rejected by the PHOL, and a new sample must be submitted with a completed requisition. table 13: Water – laboratory rejection criteria DescriPtion reason for rejection Sample Type • Bottled water with intact seal • Specimen received from an unauthorized submitter • Private citizen collected non-treated surface water or drinking water sample collected by a Private citizen from a regulated source • Specimen location from outside of Ontario Sample Requisition • Requisition received with incomplete and inaccurate information • Unique identifier(s) missing from requisition, specimen collection bottle or both • Requisition received separated from the specimen bottle with no unique identifier to link them Sample Collection • • • • • Sample collected in non-PHOL collection bottle Outdated collection kit received (Private citizen only) Insufficient volume received for testing Aesthetically unacceptable drinking water sample Interfering substances identified during testing preventing analysis Sample Transport • • • • • • • Drinking water received greater than 48 hours after collection Non potable water received greater than 1 calendar day Specimen bottle or lid damaged in transit Specimen leaked in transit Specimen frozen upon receipt Specimen indicated as collected from a hot water tap Specimen received greater than 25°C (unless from a public beach, recreational water facility or hydrotherapy pool) Broken Chain of Custody • Regulated drinking water –“Relinquished by” section of requisition not completed or of Custody sample lacked an initialed and dated seal affixed to the cap when received. • Legal water samples –“Relinquished by” section of requisition not completed and an initialed and dated seal not affixed to the cap when received P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 21 Suspected Sewage Contamination Sample Analysis Collection and Transportation Instructions Table 14 provides instruction for the use of the Sewage Sample Collection Kit which was introduced in 2007 and is to be used by board of health staff when they are investigating situations of possible sewage contamination. For health and safety reasons, any samples identified as “Suspected Sewage Contamination” that are not received in this kit will not be processed and the board of health will be requested to collect a new sample using the proper requisition and kit. The PHOL tests “Suspected Sewage Contamination Samples” for the microbiological indicator Escherichia coli. The Sewage Sample Collection Kit consists of: • A sterile bar-coded PHOL water collection bottle • A sealable biohazard bag for the sample with a pocket on the side to hold the requisition • A hard transport case labeled SEWAGE SAMPLES ONLY containing absorbent material • A soft sided blue transport bag (#TC 125-B) labeled with the laminated tag with SEWAGE SAMPLES ONLY on one side and the return address of the local PHOL on the opposite side • A “Bacteriological Analysis of Water Single Sample Requisition for Official Agencies” (see Appendix B) • An instruction sheet entitled “Collection and Transportation Procedure for Sewage Sample Submitted to the Ontario Public Health Laboratories” table 14: suspected sewage contamination samples – collection and transportation instructions Precautions samPlinG instructions 22 1. Complete the required information on the requisition. Samples will not be processed if the requisition is not completely and accurately filled in when received at the laboratory, and a new sample and completed form will be required to be submitted. 2. Remove one barcode from the bottle and apply it to the top copy of the requisition in the “Barcode” field. Samples will not be processed if the barcode is not affixed to the requisition. If the barcode is not able to be removed, write the barcode number on the form. 3. Examine the lid of the bottle. If the tamper evident ring has separated from the cap use another bottle. 4. Remove the cap. • Do not touch the inside of the lid • Do not put the lid down • Do not rinse out the bottle as this will remove the sodium thiosulfate which neutralizes the chlorine residual before testing in order to maintain bacterial viability during sample transport to the laboratory. • Do not ingest; for accidental exposure get medical attention. 5. Wearing rubber/latex gloves, collect the suspected sewage contaminated sample to the 200mL fill line. • Do not overfill. • If overfilled, remove some of the water so it is filled to 200mL line. P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table 14: suspected sewage contamination samples – collection and transportation instructions ...continued samPlinG instructions Precautions 6. Tighten the cap on the collection bottle. Leaking samples will not be processed; a new sample and requisition will be required. 7. Wipe down exterior of collection bottle with disinfectant A freshly prepared 1% solution of sodium hypochlorite, i.e.1 part household bleach to 10 parts water is recommended 8. Remove and discard rubber/latex gloves. Wash / sanitize your hands. Do not put in biohazard bag along with sewage sample. 9. Seal the sewage specimen bottle in the biohazard bag supplied. 10.Put the completed requisition in the side pocket of the biohazard bag containing the sewage sample. Do not place the requisition inside the biohazard bag with the sample. 11.Place the packaged sewage specimen in the hard transport case labeled SEWAGE SAMPLES ONLY containing absorbent material and a frozen ice pack. This container is placed inside a blue laboratory sewage transport bag (#TC 125-B). • The sewage transport bag will have a permanently attached laminated tag on the top stating in red “SEWAGE SAMPLES ONLY”. • Do not send sewage samples in any other transport container or with other environmental or medical specimens, as sample integrity cannot be ensured, resulting in the rejection of all samples submitted in this manner. 12.Store and transport samples between 1°C and 10°C (preferably 4°C) • DO NOT freeze the sample. within one calendar day of collection. • Samples must be received at the laboratory within one calendar day after collection. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 23 Legionella Investigations Legionella – Microbiological Analysis Test Menu Table 15 provides an overview of the testing available and turn around times for Legionella through the PHOL. Turn around time is defined as the number of business days to complete testing based on date of receipt in the laboratory. This turn around time definition does not apply to tests that are on-hold awaiting information to continue testing. Turn Around Times posted in this Guide are estimates for routine tests. For some tests or at times of public health emergencies, outbreaks or exigent circumstances, turn around times may be longer than what is listed. PHO/OAHPP disclaims all warranties whether express or implied in respect of the information, including the TATs provided herein. Environmental testing for Legionella will only be performed for an investigation of a confirmed clinical case and this information must be provided to the laboratory when environmental testing is requested. table 15: Legionella – microbiological analysis test menu samPle DescriPtion samPle container tests PerformeD turn arounD time Water – potable PHOL water sample bottle – one liter 5 X 200mL Legionella culture 10 – 15 days Water – non-potable PHOL water sample bottle – 200mL Legionella culture 10 – 15 days Environmental Swabs Contact the PHOL – Toronto, Environmental Microbiology Laboratory at 416-235-5716 Legionella culture 10 – 15 days Solid material Sterile plastic bag with round wire closure Legionella culture 10 – 15 days Legionella – Selection of Sampling Sites The investigation, including environmental and epidemiologic factors, should be considered in choosing the sites to be sampled to identify the source of Legionella. investigation and selection of sampling sites, but it is not a list of mandatory sampling sites. Additional resources may be found under Supporting Documentation/References. Legionella outbreaks occur because of aerosolization and inhalation of high numbers of Legionella. Investigators should try to determine where in a water system there is stagnation of water and subsequent aerosolization of stagnant water. Any dead ends in a water system may allow Legionella to grow to high numbers. Dead-ends may be disconnected fixtures where pipes are capped instead of completely removed. Any fixtures and water lines that are not used on a regular basis may allow Legionella to grow to high numbers. • Potable water outside or on the boundary of the hospital property o Treatment plant (raw and refined water) o Guard house or outlying facility if water is not fed there from hospital o Fire hydrant(s) • General potable water system for hospital o Incoming water pipe(s) o Water softener (pre and post) o Preheater (discharge side) o Primary heater o Circulating pump(s) o Holding tanks (cold water, discharge side) o Expansion tank for hot water (if possible) o Back drain on sprinkler system(s) (trap to prevent back flushing may be present and should be sampled) o Fireline where it branches off main system (may be multiple) • Pharmacy o Water used for respiratory therapy equipment Samples most likely to be positive should be sampled and submitted first. Random sampling may delay the identification of the source of the outbreak. The most obvious sampling sites would be water sources in close proximity to infected individuals. The following is a list of sampling sites recommended by the Centers for Disease Control, Atlanta, for investigating outbreaks (Barbaree JM, 1987). It can be a guide for 24 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y • Air compressor system o Vacuum water source o Positive pressure equipment side o Condensate from tanks(s) o Water separator(s) (directly off compressors) o Water source(s) near air intake(s) o Air samples where patients were ill with legionellosis • Potable water final distribution outlets o Hemodialysis water source o Before demineralizer o After demineralizer o Intensive care units o Respiratory therapy (patient rooms) o Cardiac o Services with different geographical locations o Ice maker (entry water) • Air-conditioning system o Air handling unit to service where disease occurred (drain pan) o Blowdown o Water supply • Whirlpool(s) o Whirlpool (one nearest air intake system) o Whirlpool drain • Other o Decorative fountain(s) o Creeks, ponds, and sites of stagnant water. Legionella – Environmental Sample Collection and Transportation Instructions Table 16 provides information and sampling instructions for water, environmental swabs and solid material in the investigation of Legionella. notes: • The PHOL should be notified prior to sample submission to allow for preparation of materials required for testing. Please contact the PHOL – Toronto, Environmental Microbiology Laboratory at 416-235-5716. • Samples should be stored at refrigeration temperature (2 to 6°C) and shipped to the laboratory as soon as possible. • Each sample must be labeled with the unique identifier that must also be affixed to the requisition. PHOL water bottles have barcodes attached that can be used for this purpose. Absence of a unique identifier linking sample(s) to a sampling location on a requisition will result in rejection of sample(s) by the laboratory. • Drinking water analyses are performed in outbreak situations or upon special request and MUST be submitted as NON-REGULATED requests only. table 16: Legionella – environmental sample collection and transportation instructions Legionella Investigations –Water Sampling samPlinG instructions Precautions 1. Collect water in PHO water collection bottles: For potable water, collect one liter of water. Five standard bacteriology water bottles filled to the fill line will satisfy this requirement. For non potable waters, a single bottle of 200mL is sufficient. • Taps or showers should not be allowed to run before sampling. Turn water on and allow the water to run slowly into sample bottles. • Use of Personal Protective Equipment (PPE) should be guided by local board of health internal health and safety guidelines. 2. Complete the requisition: For liquid samples collected in water bottles, use either of the following requisitions: • Bacteriological Analysis of Water – Multiple Sample Requisition for Official Agencies • Bacteriological Analysis of Water – Single Sample Requisition for Official Agencies • Drinking water analyses are performed in outbreak situations or upon special request and MUST be submitted as NONREGULATED requests only. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 25 table 16: Legionella – environmental sample collection and transportation instructions ...continued Legionella Investigations – Environmental Swab Sampling Environmental swabs can be used for Legionella outbreak investigations. These are available (for outbreaks only) from the PHOL, Toronto. The environmental swabs available from the PHOL – Toronto contain neutralizing solution as transport medium. This medium can neutralize the following sanitizers: iodophores including chlorine compounds, quaternary ammonium compounds and phenolic sanitizers. Environmental swabs are processed during outbreak investigations for the presence or absence of Legionella. samPlinG instructions Precautions 1. If a water sample has not been collected, collect one first as described in Legionella Investigations – Water Sampling. • Swabs are usually collected from shower heads or other implements that aerosolize water. 2. Remove shower head. 3. Open the sterile swab container; grasp the handle end of the swab. • Remove the swab aseptically being careful not to touch any portion that might be inserted into the vial. 4. Moisten the swab head and press out the excess solution against the interior wall of the vial with a rotating motion. 5. Use the head of the swab to scoop up any sediment that has built up inside the shower head. 6. If there is no sediment in the shower head, swab the inside of the shower head and the pipe to which the shower head was attached to pick up biofilm. For cooling towers, swabs can be used to sample any build-up of slime or biofilm on the equipment: Hold the swab handle to make a 30° angle contact with the surface. Rub the swab head slowly and thoroughly over approximately 50 cm2 of the surface three times, reversing direction between strokes. 7. After the area has been swabbed, using aseptic technique, return the swab to the vial. • Ensure the vial is closed tightly to prevent leakage and specimen rejection. 8. Complete all sections of the Environmental Bacteriology Swab Tests requisition (see Appendix E) with appropriate information to ensure accurate tracking of sampling. Legionella Investigations – Solid Material Sampling samPlinG instructions Precautions 1. Sterile plastic bags with round wire closure can be used to collect solid material as required. Such material may include filter material from air filters or water filters. • These bags are available at most board of health offices for the collection of food samples. 2. For solid material collected in plastic bags use the requisition entitled Environmental Bacteriology SwabTests (see Appendix E). 26 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Glossary – Water Terms term Definition aesthetically unacceptable drinking water Drinking water that is not clear, colourless or odourless audit sample A sample taken outside of the routine testing schedule as part of an audit background bacteria in potable water Bacteria which fail to ferment lactose on culture media designed for coliform detection. They are also know as non-target organisms in drinking water testing bottled water Potable water in commercially sealed containers chain of custody An unbroken documented chain of events from the time of sample collection until it is processed and completed cistern A reservoir, tank or container for storing or holding water compliance A sample taken to fulfil the requirements of an Ontario drinking water regulation control sample for water testing A sample taken prior to a change in a routine or prior to the application of a corrective action customer investigation An investigation resulting from a verbal or written communication by a customer Designated facility A facility as described in Ontario Regulation 170/03 Drinking Water Systems Distribution The section of a drinking water system that transports drinking water to the end user Escherichia coli (e. coli)2 E. coli are coliform bacteria. They are Gram-negative, facultatively anaerobic, non spore-forming, lactose-fermenting, rod-shaped bacteria which are oxidase negative. Approximately 95% of E. coli strains can produce the enzyme β-D-glucuronidase, which splits the substrate 5bromo-4-chloro-3-indolyl-β-D-glucuronide (i.e. B.C.I.G.) within 24-72 h at 36°C. Historically, the presence of either or both E. coli and fecal coliforms has been described as an indication of sewage or fecal contamination as they are commonly isolated from the intestinal tract of warm-blood animals. Currently, E. coli is considered to be the most specific indicator of fecal contamination in the assessment of water quality for the following reasons: • E. coli isolates are normally present in the feces of warm-blooded animals (including humans) at higher densities (107 to 108 cells per gram) than other lactose-fermenting members of the family Enterobacteriaceae. • E. coli isolates may persist for periods of time, once outside the human or warm-blooded animal intestine but they generally do not multiply in water or wastewater in temperate climates. • E. coli isolates have seldom been detected in environments which have not been contaminated by fecal wastes. In contrast, other thermotolerant organisms such as isolates of the genera Klebsiella, Enterobacter and Citrobacter, have been associated from both fecal material and other wastes including that from food and pulp and paper. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 27 Glossary – Water Terms ...continued 28 term Definition Etiological Agent The cause or origin of a disease Frozen Water at or below zero degrees C or containing obvious ice fragments Heterotrophic Plate Count (HPC), Aerobic Plate Count (APC) or Standard Plate Count (SPC) The heterotrophic plate count is a process of estimating the number of viable, heterotrophic bacteria (i.e. bacteria capable of growth aerobically on Standard Methods Agar or a similarly formulated growth medium when incubated at 35 +/- 0.5°C for 48 +/-3 hours) in water and measuring the changes that occur to bacterial populations during water treatment and distribution HPPA O. Reg. 318/08 Drinking Water Drinking water that is subject to the requirements as described in Ontario Regulation 318/08 under the Health Protection and Promotion Act until it is repealed HPPA O. Reg 319/08 Drinking Water Drinking water that is subject to the requirements as described in Ontario Regulation 319/08 under the Health Protection and Promotion Act HPPA Regulated Premises Premises/facilities regulated under HPPA, (Food premises, Recreational water places, etc.) that fall outside the scope of O. Reg. 319/08 Hydrotherapy pool Public spa as per Ontario Regulation 428/05 Public Spas Ice Potable water which has been cooled to a temperature less than 0°C Interactive Voice Response (IVR) A technology that allows a computer to interact with humans through the use of voice and dual-tone multi-frequency signaling keypad inputs. Private Citizen drinking water test results and the interpretation can be accessed by calling a toll free telephone number and keying in the sample barcode when prompted Interfering substances A substance in a water sample that either prevents the water from passing through the membrane filter during the testing process or after the incubation process, there is a substance on the membrane filter that does not allow an accurate determination of the colony count Legal sample Any laboratory specimen that has been submitted for testing to the PHO Laboratories with an intact legal seal and whose chain of custody has been maintained Municipal Drinking-Water System Refer to the Safe Drinking Water Act, 2002 Non Municipal Drinking Water System Refer to the Safe Drinking Water Act, 2002 Non Regulated Drinking Water Drinking water systems that are not captured by specific regulation where the public has access to the water and such systems are subject of an investigation under the HPPA, public health inspectors may collect drinking water samples in concurrence with the following sections of the HPPA: Section 13, Section 41, Subsections (1), (2), (4), and (5). See Table A Examples of Drinking Water that Fall Outside Ontario’s Drinking Water Regulations Non treated Water that is not subjected to disinfection or other means of removing contaminants P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Glossary – Water Terms ...continued term Definition Official Agency a) Board of health (public health unit): An official health agency established by a group of urban and rural municipalities to provide a more efficient community health program, carried out by full-time, specially qualified staff, or b) Ministry of Natural Resources Ontario Park: Ontario land dedicated to the people of Ontario and visitors for their inspiration, education, health, recreational enjoyment and other benefits with the intention that these areas shall be managed to maintain their ecological integrity and to leave them unimpaired for future generations. Refer to Provincial Parks and Conservation Reserves Act, 2006 Outbreak investigation A sample taken as part of a pubic health outbreak investigation Outbreak number The number assigned to an outbreak by public board of health staff for tracking purposes Overgrown The crowding and /or confluent and/or non-identifiable microbial growth on a plate, and there is no evidence E. coli, the culture is considered overgrown with background bacteria Overgrown with the presence of E. coli Overgrown with the presence of E. coli The crowding and /or confluent and/or non-identifiable microbial growth on a plate, but there is evidence of E. coli as well. Private Citizen A person residing in Ontario who: a) does not have access to a treated municipal drinking water supply and b) draws their drinking water from a protected source within the Province of Ontario for personal use or applies appropriate treatment to water drawn from an unprotected source Private Citizen Drinking Water Drinking water from a “single household” and private residence as defined in Ontario Regulation 171/03 Definitions of Words and Expressions Used in the Act Private Residence Refer to Ontario Regulation 171/03 Definitions of Words and Expressions Used in the Act (e.g. water source can include a well, cisterns, treated surface water, etc.). Pseudomonas aeruginosa A Gram negative, non-fermentative, oxidase positive, rod shaped bacteria, which grows well at 42°C, is actively motile, and under appropriate incubation conditions produces a fluorescent pigment and often a visible pigment. Public Beach Refer to Ontario Public Health Standards 2008 – ‘Beach Management Protocol’, 2008 or current version Recreational Water Facilities Refer Ontario Public Health Standards, 2008. ‘Recreational Water Protocol’, 2008 or as current Regulated water seal A fixture attached to the cap of a drinking water sample submitted under a drinking water regulation that must be broken before access can be obtained Relinquish To release a sample ensuring the chain of custody is not compromised Resample A sample taken from the same location. Usually in response to a adverse test result or incident Routine surveillance Observation over a group, area or system on a regular basis P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 29 Glossary – Water Terms ...continued term Definition SDWA O. Reg 170/03 Drinking Water Drinking water that is subject to the requirements as described in Ontario Regulation 170/03 Drinking Water Systems (e.g. some Municipal, Non-municipal and designated facilities) Single Household Potable water from any source which is protected from surface or ground water contamination, regardless of any filtration procedure and/or chemical disinfection applied, is aesthetically acceptable, and serves fewer than 6 private residences but not to the public. For analytical purposes, water passing through a point-of-use treatment device will be regarded as a private water source. Staphylococci sp. Staphylococci are Gram-positive cocci of the family Micrococcaceae. Staphylococcus aureus S. aureus is a facultative anaerobe of the family Micrococcaceae that produces a wide array of toxins and can coagulate rabbit plasma. Surface water Water collecting on the ground or in a stream, river, lake, etc. Suspected sewage contamination Water suspected of being contaminated by fecal material Test for Potability Total coliform and E. coli analysis Total coliforms 2 Coliforms are described as Gram-negative, non spore-forming, rodshaped bacteria capable of fermenting lactose with the production of acid and gas, within 48 hours, when grown in a lactose-containing liquid culture medium incubated at 36+/-1.0°C. The total coliform count is the quantification of colony forming units (CFU) that meet this definition (including E. coli) per 100 mL of sample. There are some lactose-fermenting strains of species within the genus Aeromonas which produce a coliform-like reaction on media used for the detection of bacterial indicators of contamination. Aeromonas species are oxidase-positive and generally fail to produce gas during lactose fermentation in liquid media. They do not, therefore, conform to the classical definition of a coliform. Regardless, they are often included in the total coliform count because the growth medium fails to differentiate this organism from the true coliforms. Some coliform bacteria are commonly isolated from the fecal material found in the intestines of humans and other warm-blooded animals (eg. E. coli) and coliforms, in general, may also be isolated from plants, soil and sediments. The Total Coliform count, therefore, does not necessarily provide specific evidence of fecal contamination. Treated Water that is subjected to disinfection or other means of removing contaminants Unauthorized Submitter – Official Agency A submitter representing an agency other than a board of health or a Ministry of Natural Resources Ontario Park Unauthorized Submitter – Private Citizen A person who submits a drinking water sample that does not meet the definition of “Private Citizen” or “Single Household” Unique identifier A sample identifier that uniquely distinguishes it from any other sample submitted. The sample barcode is used for this purpose. Water well A hole drilled or bored into the earth to obtain water 2 30 Some information taken from Ministry of the Environment’s Laboratory Services Branch method MICROMFDC-3407 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table a: examples of Drinking Water that fall outside ontario Drinking Water regulations The following list provides some examples which fall outside the scope of the Safe Drinking Water Act 2002, Drinking Water Systems Ontario Regulation 170/03 and the Health Protection and Promotion Act, Small Drinking Water Systems Regulations (i.e. O. Reg 318/08 and O. Reg 319/08). Drinking water systems that are not captured by specific regulation where the public has access to the water and such systems are subject of an investigation under the HPPA, public health inspectors may collect drinking water samples in concurrence with the following sections of the HPPA: Section 13, Section 41, Subsections (1), (2), (4), and (5). The following examples may be considered ‘drinking water systems’ in which drinking water samples must be analyzed at a licensed laboratory using licensed drinking water testing methods, unless the example is entirely a plumbing system or they are facilities with no ‘works’ that have been established for providing potable water. situation examPle Drinking water supplies that do not meet the specific criteria of the Safe Drinking Water Act 2002 or Health Protection and Promotion Act drinking water regulations • Seasonal campsite with fewer than 6 water connections, camps in unorganized territory, certain recreational camps, rental cabins with fewer than 6 units using the same water supply, etc. • Raw water that it is not for human consumption and is not distributed to the public (i.e. unfinished water in a treated drinking water system, new water mains, etc.) Facilities in the following circumstances • Serviced by private drinking water systems that require health unit approval for licensing or funding approval: Funeral homes, group and boarding homes, homes for special care, migrant farm workers, etc. Food premises in the following circumstances • Small food take out and convenience stores where there is no direct access to drinking water by the patrons, temporary food service facilities, farmers markets, etc. • Special event food premises or mobile food vending vehicles Outbreak investigations • Testing of a drinking water system as part of an outbreak investigation (e.g. Legionella, E. coli O157:H7, Salmonella, etc.), regardless if the drinking water system is regulated under drinking water regulations under the Safe Drinking Water Act 2002 or the Health Protection and Promotion Act. Plumbing in the following circumstances • Samples are taken from a building’s plumbing (i.e. when the water enters private property) although the water originated from a drinking water system under an Ontario drinking water regulation. Example - a private residence in a town or city, private apartment buildings, factory or food manufacturing plant, etc. If a sample is collected to assess the water quality and not the plumbing, then it is considered a drinking water sample and must be analyzed at a licensed laboratory using licensed drinking water testing methods. Private individual well water supplies • • • • Water Containers • Water haulage trucks (testing may be required as part of an inspection as per Drinking Water Haulage Guidance Document) • Private building water coolers • Commercial bottled water / water bottling facilities • Vending machines that dispense water, i.e. “Bottle your own water” • Cisterns not supplying systems regulated under the Safe Drinking Water Act, 2002 or the Health Protection and Promotion Act Enteric disease follow up Assisting with addressing / identifying water safety concerns Complaints Landlord and tenant matters and samples are taken of the private water supply for the issuance of a section 13 order for a violation of section 20 under the HPPA • Treatment devices for samples taken to assess the ability of a newly installed treatment process at a premise. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 31 Interpretation of Environmental Microbiological Test Results Table 17 summarizes acceptable limits and interpretation of test results for all tests performed by the PHOL for foods, water, suspected sewage contamination samples and Legionella investigations. Microbial standards for drinking water testing are based on Ontario Drinking Water Quality Standards (O. Reg 169/03) with input from the Ministry of Health and Long-Term Care Environmental Health Policy and Programs Public Health Division. Microbial standards for food testing, public beach water testing, and Legionella environmental testing are based on published evidence where available. In a foodborne outbreak investigation, interpretation is dependent on the pre-test probability of a food being contaminated with the suspected or confirmed pathogen, based on epidemiological information obtained during the investigation. For many bacterial organisms, such as E. coli O157:H7 and Listeria monocytogenes, molecular typing by pulsed field gel electrophoresis can be used to support a link between clinical and environmental isolates. table 17: interpretation of environmental microbiological test results analysis background bacteria samPle tyPe/source rePortinG limits accePtable limits Water – Potable 0 to “Overgrown” (only reported on Regulated drinking water samples submitted under an “Order” or “Approval”) < 200 per 100 mL Recreational Water Facilities and Hydrotherapy Pools Only reported if “Overgrown” N/A laboratory test interpretation: Presence of background organisms is an unusual occurrence in drinking water, which has been properly disinfected. High levels (>200 per 100 mL) reflect a deterioration in water quality and an increase in health risk potential. May include bacterial pathogens most of which are non-coliforms. When samples are heavily contaminated (i.e. overgrown) with bacteria often found in the environment, this condition interferes with the detection of coliforms or Escherichia coli that may be present in the sample. The water may be unsafe to drink unless boiled or treated. Bacillus cereus Food <100 to >2x105 per gram <103 per gram laboratory test interpretation: B. cereus is common in the environment and may be present in food in small numbers. Isolation of >105 organisms per gram of food may be associated with foodborne illness. Campylobacter jejuni Water Presence/Absence Absent laboratory test interpretation: Transmission of Campylobacter via water is epidemiologically implicated, but the organism has rarely been isolated from suspect sources. Analysis of water samples for Campylobacter should only be undertaken when there has been clinical confirmation of an outbreak and a water source has been incriminated epidemiologically. Food Presence/Absence Absent laboratory test interpretation: C. jejuni is a major cause of acute bacterial enteritis in humans. It is often present in raw food of animal origin. This organism is highly susceptible to environmental stresses and does not survive proper cooking or pasteurization. The majority of foodborne outbreaks are the result of consumption of raw, under processed or cross-contaminated foods. 32 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table 17: interpretation of environmental microbiological test results ...continued analysis Clostridium botulinum samPle tyPe/source rePortinG limits accePtable limits Food/Feces/Serum Presence/Absence Absent laboratory test interpretation: Human food poisoning is rare but case fatality rate (untreated) is high. Demonstration of neurotoxin in serum or feces is necessary to confirm diagnosis. Detection of the same neurotoxin-producing type of C. botulinum in suspect food is sufficient to implicate the food as the source of illness. Clostridium perfringens Food <100 to >2x106 per gram <100 per gram laboratory test interpretation: C. perfringens is part of the intestinal flora of all warm-blooded animals and can be found in low numbers in the environment. Food poisoning is caused by the release of enterotoxin in the intestine by sporulating organisms. A count of greater than or equal to 105 organisms per gram of food is associated with foodborne illness. Coliforms Water – Potable 0 to >80 per 100 mL Private Citizen samples: ≤5 per 100 mL Official Agency and bottled water samples: 0 per 100 mL Recreational Water Facilities and Hydrotherapy Pools <2 to > 160 per 100 mL <2 per 100 mL laboratory test interpretation: The presence of coliforms may be indicative of a contaminated water supply. Coliforms occur naturally in soil and decaying vegetation; but may also be associated with human or animal fecal contamination. Given the vulnerability of well water to external influences, such as human, environmental and agricultural impacts, it is important to test water frequently. Food <3 to >1.1 x 103 per gram <103 per gram laboratory test interpretation: Presence of coliforms in a processed, cooked, ready-to-eat food is indicative of inadequate processing or post processing contamination resulting from poor handling of the product. This acceptable limit cannot be applied to uncooked or raw foods such as salads and salad ingredients, raw fruits and vegetables, etc. Ice cream <3 to >1.1 x 103 per mL ≤10 per mL laboratory test interpretation: Presence of coliforms suggests recontamination following pasteurization but could also indicate inadequate pasteurization. escherichia coli Water – Potable 0 to >80 per 100 mL 0 per 100 mL Recreational Water Facilities and Hydrotherapy Pools <2 to > 160 per 100 mL <2 per 100 mL Public Beaches <10 to >103 per 100 mL <100 per 100 mL laboratory test interpretation: The presence of Escherichia coli may indicate fecal contamination from a human or animal source. There is a strong relationship between increased levels of Escherichia coli in recreational waters and the incidence of swimming associated gastroenteritis. Suspected Sewage Contamination <103 to >1x106 per 100 mL Not Applicable laboratory test interpretation: Escherichia coli levels in water >10 per 100 mL are indicative of fecal contamination 5 Food <3 to >1.1 x 103 per gram <3 per gram laboratory test interpretation: The presence of Escherichia coli in food is indicative of direct or indirect contamination of the food product with fecal material and thus, a potential for enteric pathogens to also be present. Certain serotypes of Escherichia coli are capable of causing outbreaks of diarrhea. e.coli o157:H7 Food Presence/Absence Absent laboratory test interpretation: The presence of E.coli O157:H7 in a processed, cooked or ready-toeat food is a definite health hazard. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 33 table 17: interpretation of environmental microbiological test results ...continued analysis Heterotrophic Plate count (HPc) samPle tyPe/source rePortinG limits accePtable limits Water – Potable <10 to >2x10 per mL <500 per mL 3 laboratory test interpretation: An HPC >500 per mL in a distribution system or other treated water is indicative of poor water quality and possible problems with the disinfection procedure. Recreational Water Facilities and Hydrotherapy pools <10 to >2x103 per mL See comments under “Laboratory Test Interpretation” laboratory test interpretation: APHA recommends for public swimming pools that not more than 15% of samples collected during any 30-d period shall have an HPC count of 200/mL. Food <103 to >2.0 x 105 per gram <105 per gram laboratory test interpretation: It is reasonable to expect properly prepared and handled ready-toeat processed or cooked foods to have an HPC <104 per gram. An HPC >105 per gram is evidence of temperature abuse – inadequate cooking or improper storage conditions. HPC cannot be applied to raw, uncooked, unprocessed foods (e.g. fruits or vegetables) or cultured products (e.g. cheese). Legionella species Taps/sinks/spas/ showers Presence/Absence Significance interpreted per investigation in consultation with medical microbiologist laboratory test interpretation: Except for high risk populations, routine environmental monitoring for Legionella is not recommended. Legionellae have predilection for sediments, slimy deposits and rubber fittings in water distribution systems. Recovery of Legionellae from >30% of different sampling sites is considered to indicate a hazard. Listeria monocytogenes Food (high risk foods, or in outbreak investigation) Presence/Absence Absent laboratory test interpretation: Reference Food Directorate, Health Canada Policy on Listeria monocytogenes in Ready-to-eat Foods, FD-FSNP 0071 April 1, 2011 pH Food 1.00 to 14.00 laboratory test interpretation: pH is a measure of food acidity, which varies with food type. Foods with a pH ≤ 3.7 will not support the growth of bacterial foodborne pathogens. However, if the pH of the food (jarred/canned products) is ≤ 4.6, all micro-organisms are inhibited with an aw ≤ 0.85. Phosphatase (alkaline phosphatase) Dairy Presence/Absence Absent laboratory test interpretation: The detection of residual alkaline phosphatase indicates a reduction in pasteurization temperature of at least 1.5°C; a 5 minute reduction in holding time; or the presence of ≥0.3% raw milk. Pseudomonas aeruginosa Recreational Water Facilities and Hydrotherapy pools 0 to >100 per 100 mL <10 per 100 mL Water – Potable/Bottled 0 to >100 per 100 mL 0 per 100 mL laboratory test interpretation: P. aeruginosa can be found in sewage effluents at levels of up to 105 per 100 mL.Well operated pools should not normally contain P. aeruginosa. If the count is over 10 P. aeruginosa per 100 mL, repeat testing should be undertaken. Where repeated samples contain P. aeruginosa the filtration and disinfection processes should be examined to determine whether there are areas within the pool circulation where the organism is able to multiply. Where counts exceed fifty, pool closure should be considered. P. aeruginosa is a primary cause of ear, eye and skin infections among swimmers. 34 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table 17: interpretation of environmental microbiological test results ...continued analysis Salmonella species samPle tyPe/source rePortinG limits accePtable limits Water Presence/Absence Absent laboratory test interpretation: When present, Salmonella are usually in low numbers in water. Large sample volumes are necessary to allow for a concentration procedure. Presence of Salmonella in potable water should not be tolerated, as such conditions allow the potential of the organism to spread and multiply and become a significant health risk. Food Presence/Absence Absent laboratory test interpretation: The presence of Salmonella in a processed, cooked or ready-to-eat food is a definite health hazard. The presence of Salmonella in a raw product, particularly poultry, beef or pork, to be subjected to further processing prior to consumption, is not unusual. Staphylococcus aureus Recreational Water Facilities and Hydrotherapy Pools 0 to >100 per 100 mL <50 per 100 mL Water – Potable/ Bottled 0 to >100 per 100 mL 0 per 100 mL laboratory test interpretation: S. aureus is a major pathogen responsible for purulent infections of the skin, eyes and ears. Its presence in swimming pools and hydrotherapy pools is a good index of the health hazard associated with a high bather density. Food <100 to >2x105 per gram <100 per gram laboratory test interpretation: S. aureus is a major foodborne disease agent causing nausea, vomiting, abdominal cramps and diarrhea. Preformed toxin in foods causes an onset of symptoms within one to eight hours of ingestion of food. Recovery usually occurs within 24 hours. To be implicated in foodborne disease, a suspect food should contain >105 S. aureus per gram. An epidemiologically implicated food may be tested for staphylococcal enterotoxin. The presence of enterotoxin is a definitive diagnosis. Detection of the same enterotoxin-producing isolates from a suspect food and related clinical specimens is strong evidence that the food is directly implicated. total Gram negative count (tGnc) Food <103 to >2x105 per gram <103 per gram laboratory test interpretation: TGNC has same significance as presence of coliforms. Elevated TGNC should not be detected in cooked or processed ready-to-eat foods. Absence of gram negative organisms in food sample is another indicator of food safety. Vibrio parahaemolyticus Vibrio cholerae non-01 Vibrio cholerae Vibrio fluvialis Vibrio vulnificus Vibrio mimicus Food Presence/Absence Absent laboratory test interpretation: May be the result of insufficient cooking or recontamination from mishandling. Implicated foods include crab, oysters, shrimp and lobster. Organisms can be recovered from brackish coastal waters, sediment and sea-life in temperate estuarine environments. Specialized culture techniques must be used to recover vibrios from food samples. Water activity (aw) Food N/A N/A laboratory test interpretation: The availability of water for microbial, enzymatic or chemical activity determines the shelf life of foods. This water availability is measured as water activity (aw). Water activity is measured on a scale of 0 to 1, where 0 indicates no water and 1 indicates all water. For a food to be considered safe to store at room temperature, it should have an aw ≤ 0.85. Bacterial foodborne pathogens are inhibited at this aw; however, spoilage microorganisms would be inhibited below aw 0.6. Yersinia enterocolitica Food/Water Presence/Absence Absent laboratory test interpretation: Pathogenic biotypes have rarely been isolated from incriminated foods or water, although Yersinia may be successfully isolated from clinical specimens. Isolation of a pathogenic biotype from a ready-to-eat food can implicate that food as a vehicle of transmission in a Yersinia outbreak. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 35 Ontario Public Health Standards and Supporting Legislation • Ontario Public Health Standards, 2008. ‘Beach Management Protocol’, 2008 or as current. http://www.health.gov.on.ca/en/pro/programs/publichealth/oph_standards/ophsprotocols.aspx • Ontario Public Health Standards, 2008. ‘Drinking Water Protocol’, 2008 or as current http://www.health.gov.on.ca/en/pro/programs/publichealth/oph_standards/ophsprotocols.aspx • Ontario Public Health Standards, 2008. ‘Food Safety Protocol’, 2008 or as current. http://www.health.gov.on.ca/en/pro/programs/publichealth/oph_standards/ophsprotocols.aspx • Ontario Public Health Standards, 2008. ‘Recreational Water Protocol’, 2008 or as current http://www.health.gov.on.ca/en/pro/programs/publichealth/oph_standards/ophsprotocols.aspx • Health Protection and Promotion Act, 1990. Ontario Regulation 318/08 (Transitional - Small Drinking Water Systems. http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_080318_e.htm • Health Protection and Promotion Act, 1990. Ontario Regulation 319/08 (Small Drinking Water Systems. http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_080319_e.htm • Health Protection and Promotion Act, 1990. Ontario Regulation 428/05 (Public Spas). http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_050428_e.htm • Health Protection and Promotion Act, 1990. Regulation 562 (Food Premises). http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_900562_e.htm • Health Protection and Promotion Act, 1990. Regulation 565 (Public Pools). http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_900565_e.htm • Ontario Water Resources Act, 1990. Regulation 903 (Wells). http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_900903_e.htm • Safe Drinking Water Act, 2002. http://www.e-laws.gov.on.ca/html/statutes/english/elaws_statutes_02s32_e.htm • Safe Drinking Water Act, 2002. Ontario Regulation 169/03 (Ontario Drinking Water Quality Standards). http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_030169_e.htm • Safe Drinking Water Act, 2002. Ontario Regulation 170/03 (Drinking Water Systems). http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_030170_e.htm • Safe Drinking Water Act, 2002. Ontario Regulation 243/07 (Schools, Private Schools and Day Nurseries). http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_070243_e.htm • Safe Drinking Water Act, 2002. Ontario Regulation 248/03 (Drinking Water Testing Services). http://www.e-laws.gov.on.ca/html/regs/english/elaws_regs_030248_e.htm 36 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Supporting Documentation/References • APHA. 2001. Compendium of Methods for the Microbiological Examination of Foods. 4th ed. American Public Health Association, Washington, D.C. • APHA. 2012. Standard Methods for the Examination of Water and Wastewater. 22nd ed. American Public Health Association, Washington. D.C. http://www.standardmethods.org • Barbaree, J.M., G.W. Gorman, W.T. Martin, B.S. Fields, and W.E. Morrill. 1987. Protocol for sampling environmental sites for Legionella. Appl. Environ. Microbiol. 53:1454-1458. • Canadian Food Inspection Agency Policy on the Control of Listeria monocytogenes in Ready-to-Eat (RTE) Meat and Poultry Products http://www.inspection.gc.ca/english/fssa/meavia/man/ch4/annexhe.shtml • Food and Drug Administration, USA, 1998. Bacteriological Analytic Manual, 8th edition. http://www.fda.gov/Food/ScienceResearch/LaboratoryMethods/BacteriologicalAnalyticalManualBA M/default.htm. Accessed February 14, 2010. • Health Canada. 2004. Fungal Contamination in Public Buildings: Health Effects and Investigation Methods. http://hc-sc.gc.ca/ewh-semt/pubs/air/fungal-fongique/index-eng.php • Health Canada. 2004. Policy on Listeria monocytogenes in Ready-to-Eat Foods. FD-FSNP 0071 http://www.hc-sc.gc.ca/fn-an/legislation/pol/policy_listeria_monocytogenes_2011-eng.php • Health Canada. 1999. The Compendium of Analytical Methods. http://www.hc-sc.gc.ca/fn-an/res-rech/analy-meth/microbio/index-eng.php • Health Inspector’s Guide to the Principles and Practices of Environmental Bacteriology – 1989 – Editor: M.H.Brodsky, Chief Environmental Bacteriology • Health Inspector’s Guide to the Principles and Practices of Environmental Microbiology – 1997– Editor: M.H.Brodsky, Chief Environmental Bacteriology • Heymann DL, ed. (2008). Control of Communicable Diseases manual, 19th ed. Washington, DC, American Public Health Association • Instructions For Official Agencies Submitting Water Samples to the Public Health Ontario Laboratories http://www.oahpp.ca/services/water-testing.html • Laboratory Guide for Gastroenteritis Outbreaks (2008) Public Health Laboratories, Ontario Agency for Health Protection and Promotion – see website for most current version http://www.oahpp.ca/services/documents/specimen-collection-guide/gastro_full_20080301.pdf • Ministry of the Environment. Practices for the Collection and Handling of Drinking Water Samples. http://www.portal.gov.on.ca/drinkingwater/stel01_046911.pdf • PHO; Legionella workshop, Questions and Answers, 2012 http://www.oahpp.ca/resources/documents/presentations/2012june25/PHO%20Legionella%20Workshop%20June%202012%20-%20Q+A.pdf • SMS Environmental. http://www.sms-environmental.co.uk/swimming_pool_water.html#pseudomonas • Specimen Collection Guide – Public Health Ontario Laboratories http://www.oahpp.ca/services/specimen-collection-guide.html • WHO; Legionella and the prevention of legionellosis, 2007 http://www.who.int/water_sanitation_health/emerging/legionella.pdf • World Health Organization (2008). Foodborne Disease Outbreaks: Guidelines for Investigation and Control. Geneva, Switzerland, 2008 http://www.who.int/foodsafety/publications/foodborne_disease/fdbmanual/en/index.html P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 37 Contributors Dr. vanessa allen – Medical Microbiologist, Enteric, Environmental, Molecular Surveillance, STI and Syphilis, PHO Peter boleszczuk – Head Technologist, Environmental Microbiology, PHO Helen Doyle – Manager of Environmental Health. Community and Health Services Department, Regional Municipality of York sandy edelsward – Program Coordinator, Drinking Water Testing, PHO Dr. anna majury – Regional Microbiologist and Assistant Professor, PHO anne maki – Manager, Enteric, Environmental, Molecular Surveillance and STI, PHO allana murphy – Operational Lead, Environmental Laboratory, PHO 38 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Appendices Appendix A: Supplies Board of health staff should ensure that environmental sample collection and submission supplies are readily available. If further supplies are required, they can be obtained from the PHO – Regional Laboratory or from the Toronto Laboratory Warehouse at 416-235-5820. Supplies will be shipped within 1 – 5 days of request. Catalogue numbers are as follows: Water: cat.no. item format L-4020 Bacteriological Analysis of Water – Single Sample Requisition for Official Agencies Pkg. of 125 L-3172 Bacteriological Analysis of Water – Multiple Sample Requisition for Official Agencies Pkg. of 125 N-0040 Kit – Water – Bacteriology Test Private Citizen Drinking Water Collection Kits Box of 125 TC 125-B Sewage Collection Kits Blue Transport Bag M-5030 Bag – Stomacher Sterile plastic sample bag with round wire closure Request amount required L-8001 Seal – Regulated water Pkg. of 200 L-8002 Seal – Legal Pkg. of 50 item format L-3180 Form – Food Bacteriology Pkg. of 125 M-5030 Bag – Stomacher Sterile plastic sample bag with round wire closure Box of 250 food: cat.no. environmental swabs: cat.no. item format L-4004 Data Sheet – Environmental Swab Test Environmental Bacteriology Swab Tests requisition Pkg. of 250 Contact the PHOL – Toronto, Environmental Laboratory at 416.235.5716 Environmental Swabs (test requisition included) As requested P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 39 Appendix B: Laboratory Submission Forms Refer to the PHO website for the most current version of the forms listed below. http://www.oahpp.ca/resources/laboratory-materials.html a. Bacteriological Analysis of Water – Single Sample Requisition for Official Agencies b. Bacteriological Analysis of Water – Multiple Sample Requisition for Official Agencies c. Bacteriological Analysis of Drinking Water for Private Citizen, SINGLE HOUSEHOLD ONLY D. Food Bacteriology e. Environmental Bacteriology Swab Tests f. Potability of Water Release Form G. Autorisation De Divulguer Des Renseignements Sur La Potabilité De L’eau H. Ontario Agency for Health Protection and Promotion Legal Seal i. Ontario Agency for Health Protection and Promotion Regulated Water Seal 40 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y a. bacterioloGical analysis of Water – sinGle samPle requisition for official aGencies Barcode Date/Time Received PHL No. Bacteriological Analysis of Water – Single Sample Requisition for Official Agencies FOR DRINKING WATER: THE REGULATION STATUS OF THE SAMPLE MUST BE INDICATED. IF REGULATED, ALL NON-SHADED AREAS MUST BE COMPLETED OR THE SAMPLE WILL NOT BE ANALYZED BY THE LABORATORY AND ANOTHER SAMPLE WILL HAVE TO BE SUBMITTED. A unique identifier (i.e. barcode) must be present on both the bottle and requisition when received at the laboratory or the sample will not be processed Official Agency Address Owner of the Water Supply Agency Name: Facility: Bldg. No., Street, R.R., Box No. Bldg. No., Street, R.R., Box No. City, Town City, Town Postal Code Province Submitted By: Submitted To: Reason for Sampling Sample Information-Drinking Water Date Collected: hh : mm Time Collected: Collected By: AM PM Tel: (Working hrs.): Fax: Waterworks No.: Type of Drinking Water Systems (Check all applicable boxes) Contact Name(s): Public Health Lab Comments/Additional Information: Mandatory: tick one box HPPA O. Reg 319/08 HPPA Regulated Premises Non Regulated Private Residence SDWA O. Reg 170/03 Postal Code Province ( Control Audit Compliance Resample Complaint Investigation Outbreak Investigation Not assigned Assigned Outbreak Investigation ) Etiological Agent if Known: Test for Etiological Agent* *Call laboratory before sampling Ground Water (i.e. well) Cistern Surface Water Distribution Bottled Water Other: Free or combined chlorine residual (mg/L): Treatment Non-treated Treated Tests Performed ∆ Date Collected: Time Collected: Collected By: Escherichia coli (Cfu) per 100mL* Date Read 100mL* AM PM Public Beach ( Circle one ) Recreational Water Facility / Hydrotherapy Pool Suspected Sewage Contamination Other * (Please specify): *Call laboratory before sampling For Regulated Drinking Water or Legal Samples: Relinquished By: Relinquished By: Date: ∆ Background (Cfu) per Reported By hh : mm Sampling Site: HPC test Requested ∆ Total Coliforms (Cfu) per 100mL* Count Or, Test for Potability Sample Information-Non-Potable All potable samples must be <25°C when received at the lab. Samples must be received in the lab within 6 hours of collection if not refrigerated. Refrigerated non-potable samples must be received in the laboratory within 1 calendar day of collection and all drinking water must be received in the laboratory within 48 hours of collection (time of collection must be indicated). For Laboratories Only if assigned, indicate number Outbreak Number: Source of Drinking Water Circle one Sampling Site: (After Hours) For Lab Use: (Print Name) Time: (Signature) Date: Received By: Time: Laboratory Comments / Date Reported Pseudomonas aeruginosa (Cfu) per 100mL* Staphylococcus aureus (Cfu) per 100mL* Heterotrophic plate count (HPC) (Cfu) per mL** Other: per mL ∆ 4318-44 (12/11) Presumptive Staphylococci (Cfu) per 100mL* Authorized By: (Technologist) *Analysis by Membrane Filtration: **Analysis by Spread Plate. = Accredited test (drinking water) These results relate only to the sample tested. This information is being collected in compliance with the requirements of the Safe Drinking Act, 2002 and it’s regulations, and it will only be used for the purposes for which it is collected. Public Health Ontario is subject to the Freedom of Information and Protection of Privacy Act and any information in its records may be subject to disclosure by the Ministry pursuant to the Freedom of Information and Protection of Privacy Act. ∆ End of report P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 41 42 4321-44 (05/12) if assigned, indicate number Waterworks No.: Fax: Tel: (After hrs.): Tel: (Working hrs.): Contact Name(s): Province City, Town Bldg. No., Street, R.R., Box No. Facility Owner of the Water Supply Postal Code ( Circle one ) AM PM ( Circle one *Call laboratory before sampling Other* (Please specify) Suspected Sewage Contamination Recreational Water Facility / Hydrotherapy Pool Public Beach Sampling site: Collected by: Time Collected: hh : mm Date Collected: ) Sample Information - Non-Potable *Call laboratory before sampling Test for Etiological Agent* Or, Test for Potability Etiological Agent if Known: Control Audit Compliance Resample Complaint Investigation Outbreak Investigation (complete section below) Outbreak Number: Reason for Sampling Mandatory: tick one box HPPA O. Reg 319/08 HPPA Regulated Premises Non Regulated Private Residence SDWA O. Reg 170/03 Type of Drinking Water Systems Ground Water (i.e. well) Cistern Surface Water Distribution Bottled Water (Please Specify) Other: Treatment Non-treated Treated Source of Drinking Water Sampling Site: Collected By: AM Time Collected: hh : mm PM Date Collected: Ñ = Accredited test (drinking water) Assigned Not assigned Postal Code Public Health Lab (Please Print) Comments/Additional Information: Submitted to: Submitted by: Province City, Town Bldg. No., Street, R.R., Box No. Agency Name Barcode Time: (Signature) (Print Name) Time: Received By: Authorized By: (Technologist) Date: For Lab Use: Date Read: Reported By: ✓ Free or HPC combined chlorine Requested residual (mg/L) Ñ Total Coliforms E. coli Ñ Background Ñ Date Reported: P. aeruginosa Presumptive S. aureus Staphylococci on 1mL. Vol. by Spread Plate Bacterial Counts (Cfu) Based on 100mL Vol. By Membrane Filtration Ñ HPC (Cfu) Based End of report Lab. No./ Date & Time Received Sampling Precautions: - All potable samples must be <25°C when received at the lab. Samples must be received in the lab within 6 hours of collection if not refrigerated. - Refrigerated non-potable samples must be received in the laboratory within 1 calendar day of collection. - All drinking water must be received in the laboratory within 48 hours of collection. - Time of collection must be indicated. These results relate only to the sample tested. This information is being collected in compliance with the requirements of the Safe Drinking Act, 2002 and its regulations, and it will only be used for thepurposes for which it is collected. Public Health Ontario is subject to the Freedom of Information and Protection of Privacy Act and any information in its records may be subjectto disclosure by the Ministry pursuant to the Freedom of Information and Protection of Privacy Act. Date of Analysis: Laboratory Comments: Date: Relinquished By: Relinquished By: For Regulated Drinking Water or Legal Samples: Identification of Collection Site & Time Collected FOR DRINKING WATER: THE REGULATION STATUS OF THE SAMPLE(S) MUST BE INDICATED. IF REGULATED, ALL NON-SHADED AREAS MUST BE COMPLETED OR THE SAMPLE(S) WILL NOT BE ANALYZED BY THE LABORATORY AND ANOTHER SAMPLE(S) WILL HAVE TO BE SUBMITTED. A UNIQUE IDENTIFIER (I.E. 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ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 47 H. ontario aGency for HealtH Protection anD Promotion leGal seal i. ontario aGency for HealtH Protection anD Promotion reGulateD Water seal 48 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Appendix C: Major Foodborne Diseases: General Features Information extracted from World Health Organization (2008). Foodborne Disease Outbreaks: Guidelines for Investigation and Control. Geneva, Switzerland, 2008 table 18: major foodborne Diseases – clinical features, mode of transmission and associated High risk foods etioloGic aGent Bacillus cereus (Bacterial toxin) incubation PerioD symPtoms a) Diarrheal syndrome: 8 – 16 hours a) Diarrheal syndrome: acute diarrhea, nausea and abdominal pain. b) Emetic syndrome: 1 – 5 hours b) Emetic syndrome: acute nausea, vomiting and abdominal pain and sometimes diarrhea. mode of transmission and associated foods: Ingestion of food that has been stored at ambient temperatures after cooking, permitting the growth of bacterial spores and toxin production. Many outbreaks (particularly those of the emetic syndrome) are associated with cooked or fried rice that has been kept at ambient temperature. foods involved include: Starchy products such as boiled or fried rice, spices, dried foods, milk, dairy products, vegetable dishes, and sauces. Campylobacter jejuni Typically 2 – 5 days (range 1 – 11 days) Fever, severe abdominal pain, nausea and diarrhea which can vary from slight to profuse and watery sometimes containing blood or mucus. mode of transmission and associated foods: Principally through ingestion of contaminated food. Main food sources are raw milk and raw or undercooked poultry. Spread to other foods by cross-contamination or contamination with untreated water; contact with animals or birds. Other sources of transmission are contact with live animals (pets and farm animals). Person-to-person transmission occurs during the infectious period that ranges from several days to several weeks. foods involved include: Raw milk, poultry, beef, pork and drinking-water. Clostridium botulinum 12 – 36 hours (range several hours to 8 days) Vomiting, abdominal pain, fatigue, muscle weakness, headache, dizziness, ocular disturbance (blurred or double vision, dilated pupils, unreactive to light), constipation, dry mouth and difficulty in swallowing and speaking, and ultimately paralysis and respiratory or heart failure. mode of transmission and associated foods: Ingestion of toxin pre-formed in food. This may occur when raw or under-processed foods are stored in anaerobic conditions that allow growth of the organism. Most outbreaks are due to faulty preservation of food (particularly in homes or cottage industries), e.g. canning, fermentation, curing, smoking, or acid or oil preservation. foods involved include: Vegetables, condiments (e.g. pepper), fish and fish products, meat and meat products, honey, fruit and vegetable juices. Several outbreaks have occurred as a result of consumption of uneviscerated fish, garlic in oil, and baked potatoes. Clostridium perfringens 8 – 24 hours Abdominal pain, diarrhea, rarely vomiting and fever. mode of transmission and associated foods: Illness usually caused by cooked meat and poultry dishes subject to time/temperature abuse. Dishes are often left for too long at ambient temperature to cool down before storage, or cooled inadequately. This allows spores that survive the cooking process to germinate and grow, producing large numbers of vegetative cells. If a dish is not reheated sufficiently before consumption, the vegetative cells can cause illness. foods involved include: Meat and poultry (boiled, stewed or casseroled). Cryptosporidium parvum 2 – 4 days Persistent diarrhea, nausea, vomiting and abdominal pain, sometimes accompanied by an influenza-like illness with fever. mode of transmission and associated foods: Spread through the fecal-oral route, person-to-person contact or consumption of fecally contaminated food and water, bathing in contaminated pools. foods involved include: Raw milk, drinking-water and apple cider. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 49 table 18: major foodborne Diseases – clinical features, mode of transmission and associated High risk foods ...continued etioloGic aGent incubation PerioD symPtoms a) Enteropathogenic E. coli (EPEC) a) EPEC: 1 – 6 days; as short as 12 – 36 hours a) EPEC adheres to the mucosa and changes its absorption capacity, causing vomiting, diarrhea, abdominal pain and fever. b) Enterotoxigenic E. coli (ETEC), producing a heat-labile LT) and a heat-stable (ST) enterotoxin b) ETEC: 1 – 3 days; as short as 10–12 hours b) ETEC mediates its effects by enterotoxins. Symptoms include diarrhea (ranging from mild to a severe, cholera-like syndrome), abdominal cramps and vomiting, sometimes leading to dehydration and shock. c) Enteroinvasive E. coli (EIEC) c) EIEC: 1 – 3 days; as short as 10–18 hours c) EIEC causes inflammatory disease of the mucosa and submucosa by invading and multiplying in the epithelial cells of the colon. Symptoms include abdominal pain, vomiting and watery diarrhoea (in <10% of cases stools may become bloody and contain mucus). escherichia coli mode of transmission and associated foods: a – c) EPEC, ETEC, EIEC: consumption of food and water contaminated with fecal matter. Time/temperature abuse of such foods increases risk of illness. Up to 25% of infections in infants and young children in developing countries are due to E. coli, in particular ETEC and EPEC (10 – 20% and 1 – 5% of cases at treatment centres, respectively). ETEC is a major cause of traveller’s diarrhea in developing countries. d) Enterohaemorrhagic E. coli (EHEC) or verocytotoxinproducing E. coli (VTEC), also referred to as Shiga-toxin producing E. coli (STEC), of which the most commonly recognized is E. coli O157. d) EHEC: 3 – 8 days, median of 4 days d) EHEC causes abdominal cramps and watery diarrhea that may also develop into bloody diarrhea (hemorrhagic colitis). Fever and vomiting may also occur. mode of transmission and associated foods: d) EHEC is transmitted mainly through consumption of foods such as raw or undercooked ground-meat products and raw milk from infected animals. Fecal contamination of water and other foods, as well as cross-contamination during food preparation, will also lead to infection. foods involved with the transmission of vtec: Include ground (minced) meat, raw milk, and vegetables. Secondary transmission (person-to-person) may also occur during the period of excretion of the pathogen which is less than a week for adults but up to 3 weeks in one-third of affected children. giardia lamblia 7 – 10 days (range 4 – 25 days) Diarrhea (which may be chronic and relapsing), abdominal cramps, fatigue, weight loss, anorexia and nausea. Symptoms may be caused by a protein toxin. mode of transmission and associated foods: Infected individuals excrete Giardia cysts in large numbers. Illness is spread by fecal-oral route, person-to-person contact or fecally contaminated food and water. Cysts have been isolated from lettuces and fruits such as strawberries. Infection also associated with drinking-water from surface waters and shallow wells. foods involved include: Water, home-canned salmon, fruit and vegetables and noodle salad. Hepatitis a 25 – 28 days (range 2 – 6 weeks) Loss of appetite, fever, malaise, abdominal discomfort, nausea and vomiting, followed by symptoms of liver damage (passage of dark urine, pale stools, jaundice). mode of transmission and associated foods: Spread by fecal-oral route, primarily person-to-person. Can also be transmitted through food and water as a result of sewage contamination or infected foodhandlers. Risk of transmission is greatest during the second half of the incubation period until a few days after the appearance of jaundice. foods involved include: Shellfish, raw fruit and vegetables, bakery products. 50 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y table 18: major foodborne Diseases – clinical features, mode of transmission and associated High risk foods ...continued etioloGic aGent Listeria monocytogenes incubation PerioD symPtoms 3 – 70 days Influenza-like symptoms such as fever, headache and occasionally gastrointestinal symptoms. mode of transmission and associated foods: A substantial proportion of cases of listeriosis are foodborne. foods involved include: Raw milk, soft cheese, meat-based paste, jellied pork tongue, raw vegetables and coleslaw. Salmonella species 6 – 48 hours, occasionally up to 4 days The principal symptoms are fever, headache, nausea, vomiting, abdominal pain and diarrhea. mode of transmission and associated foods: Main route of transmission is by ingestion of the organisms in food (milk, meat, poultry, eggs) derived from infected food animals. Food can also be contaminated by infected food-handlers, pets and pests, or by cross-contamination as a result of poor hygiene. Contamination of food and water from the feces of an infected animal or person may also occur. Problems caused by initial contamination may be exacerbated by prolonged storage at temperatures at which the organism may grow. Direct person to-person transmission may also occur during the course of the infection. foods involved include: Unpasteurized milk, raw eggs, poultry, meat, spices, salads and chocolate. Salmonella typhi and Salmonella paratyphi types a–c. 10 – 20 days (range 3 days to 8 weeks) Systemic infections characterized by high fever, abdominal pains, headache, vomiting, diarrhea followed by constipation, rashes and other symptoms of generalized infection. mode of transmission and associated foods: Ingestion of food and water contaminated with fecal matter. Food-handlers may carry the pathogen and be a source of food contamination. Secondary transmission may also occur. food associated with salmonella typhi include: Prepared foods, dairy products (e.g. raw milk), meat products, shellfish, vegetables, and salads. Shigella dysenteriae S. flexneri, S. boydii, S. sonnei 1 – 3 days, up to 1 week for S. dysenteriae Abdominal pain, vomiting, fever, diarrhea ranging from watery (S. sonnei) to dysenteric with bloody stools, mucus and pus (S. dysenteriae and, to a lesser extent S. flexneri and S. boydii). mode of transmission and associated foods: Food and water contaminated with fecal matter. Person-toperson transmission through the fecal–oral route is an important mode of transmission. Food can be contaminated by food-handlers with poor personal hygiene or by use of sewage/wastewater for fertilization. foods involved include: Uncooked foods that have received extensive handling, such as mixed salads and vegetables, water and raw milk. Staphylococcus aureus 2 – 6 hours Intoxication, sometimes of abrupt and violent onset. Severe nausea, cramps, vomiting and prostration, sometimes accompanied by diarrhea. mode of transmission and associated foods: Consumption of foods containing the toxin. Foods are contaminated by food-handlers. If storage conditions are inadequate, the bacteria may multiply to produce toxin. Intoxication is often associated with cooked food e.g. meat, in which competitive bacteria have been destroyed. foods involved include: Prepared foods subject to handling in their preparation (ham, chicken and egg salads, cream-filled products, ice cream, cheese). Vibrio cholerae o1 and o139 1 – 3 days Profuse watery diarrhea, which can lead to severe dehydration, collapse and death within a few hours unless lost fluid and salt are replaced; abdominal pain and vomiting. mode of transmission and associated foods: Food and water contaminated through contact with fecal matter or infected food handlers. Contamination of vegetables may occur through sewage or wastewater used for irrigation. Person-to-person transmission through the fecal-oral route is also an important mode of transmission. foods involved include: Seafood, vegetables, cooked rice and ice. P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 51 table 18: major foodborne Diseases – clinical features, mode of transmission and associated High risk foods ...continued etioloGic aGent Vibrio parahaemolyticus incubation PerioD symPtoms 9–25 hours, up to 3 days Profuse watery diarrhea, abdominal pain, vomiting, and fever. A dysenteric syndrome has been reported from some countries, particularly Japan mode of transmission and associated foods: Associated with consumption of raw or undercooked fish and fishery products or cooked foods subject to cross contamination from raw fish. Vibrio vulnificus 12 hours – 3 days Profuse diarrhea with blood in stools. Organism is associated with wound infections and septicaemia may originate from the gastrointestinal tract or traumatized epithelial surfaces. mode of transmission and associated foods: All known cases are associated with seafood, particularly raw oysters. Yersinia enterocolitica 24 – 36 hours (range 1 – 11 days) Abdominal pain, diarrhea, mild fever, sometimes vomiting mode of transmission and associated foods: Illness is transmitted through consumption of pork products (tongue, tonsils, gut), cured or uncured, as well as milk and milk products. viral gastroenteritis Many different viruses can cause viral gastroenteritis, including adenoviruses, coronaviruses, rotaviruses, parvoviruses, caliciviruses and astroviruses. Those viruses most commonly associated with foodborne outbreaks are norovirus and hepatitis A. 15 – 50 hours Diarrhea and vomiting, which is often severe and projectile with sudden onset. mode of transmission and associated foods: Gastroenteritis viruses usually spread by fecal–oral route. Food and drinking-water may be contaminated either at source when exposed to sewage/wastewater in the environment or used for irrigation, or by an infected food-handler. Filter-feeding shellfish most common food contaminated at source, but a wide range of different cooked and uncooked foods have been implicated in secondary contamination by food-handlers. 52 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y Appendix D: List of Tables table 1: Food – Microbiological Analysis Test Menu – Indicator Bacteria table 2: Food – Microbiological Analysis Test Menu – Foodborne Pathogens table 3: Food – Microbiological Analysis Test Menu – Physiochemical Tests table 4: Food – Microbiological Analysis Test Menu – Molecular Typing table 5: Food – Microbiological Analysis Test Menu – Referred Tests table 6: Food – Collection and Transportation Instructions table 7: Food – Laboratory Rejection Criteria table 8: Sampling Instruction for Environmental Swabs in Foodborne Outbreak Investigations table 9: Water – Microbiological Analysis Test Menu table 10: Water – Microbiological Analysis Test Menu – Pathogen Specific Analyses table 11: Water – Test Requisition Requirements table 12: Water – Collection and Transportation Instructions table 13: Water – Laboratory Rejection Criteria table 14: Suspected Sewage Contamination Samples – Collection and Transportation Instructions table 15: Legionella – Microbiological Analysis Test Menu table 16: Legionella – Environmental Sample Collection and Transportation Instructions table 17: Interpretation of Environmental Microbiological Test Results table 18: Major Foodborne Diseases - Clinical Features, Mode of Transmission and Associated High Risk Foods P ublic Hea lt H insP ec t o r ’s G uiD e t o t He P rinc iP les anD P r a c t ic es o f env iro nm ent al mic ro bio lo G y 53 Notes 54 P ublic Healt H insP ec t o r ’s G uiD e t o t He P r inc iP les anD P r ac t ic es o f env ir o nm ent al m ic ro bio lo G y february 2013