AGR-WATE71-08 · Lesson 3 · 73 clock hours · lab
Sampling, Laboratory Tasks, and Regulatory Recordkeeping
Objective. The student will collect representative water or wastewater samples using correct technique and chain-of-custody documentation, perform or assist with routine on-site analyses, and accurately complete all required regulatory operating records with no critical errors.
⚠ Pending professional review
This lesson, its worked examples and its practice questions has not yet been verified by a licensed professional in the field or by a certification or approval body. It is a study draft and may contain errors. Do not use it as instructions for work on a job site or on live equipment. Always follow your instructor, your supervising professional, and current official references and regulations.
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Why Sampling, Lab Work, and Recordkeeping Matter
Every permit limit, treatment decision, and regulatory report rests on two things: a sample that truly represents what is in the water, and a record that honestly captures what happened. A flawed sample or a careless entry can cause a facility to miss a violation, report false data to regulators, or make the wrong treatment adjustment. State licensing boards and the EPA treat falsified or negligent records as serious violations. As a licensed operator, your signature on a report is a legal declaration that the information is accurate.
Collecting Representative Samples
Grab samples capture conditions at one moment in one place. Use them when you need a snapshot—for example, chlorine residual at the distribution system tap or influent pH before a treatment step.
Composite samples blend multiple grab sub-samples collected over time (or at multiple locations) to average out short-term swings. They are common for daily BOD and TSS monitoring at wastewater facilities.
Before you collect any sample, confirm three things with your supervisor and the lab's standard operating procedure (SOP):
1. Container type – Some analytes require glass; others require plastic. Containers may be pre-preserved by the lab.
2. Preservation method – Temperature (ice to ≤6 °C is common), chemical addition (such as sulfuric acid for BOD or ammonia samples), or keeping samples in the dark may all be required.
3. Holding time – The maximum time from collection to analysis. Exceeding the holding time invalidates the sample. Write the collection time on the label immediately.
Collect samples away from foam, dead spots, and the very surface or bottom unless the method specifically requires otherwise. Rinse the container twice with sample water unless it is pre-preserved or sterile (never rinse a coliform container). Label every container before you fill it: sample location, date, time, your name, and preservative added.
Chain-of-Custody (COC) Documentation
A chain-of-custody form is the legal record of who handled the sample from the moment of collection to the moment of analysis. Fill in every field: sample ID, location, collection date and time, preservative, required analyses, collector's name, and temperature at collection. Each person who receives the sample signs and dates the form. Seal sample containers with custody seals if required. Do not let samples leave the site without a completed, signed COC. Your supervisor must review the form before release.
On-Site Laboratory Tests
Many critical measurements are made in the field or in the plant lab because results are needed immediately for process control. Common tests include:
- pH – Use a calibrated pH meter. Calibrate with at least two buffer solutions that bracket the expected range before each use. Rinse the probe with deionized water between samples.
- Turbidity – Calibrate the turbidimeter with standards traceable to Formazin or AMCO-AEPA standards. Read in nephelometric turbidity units (NTU).
- Chlorine residual – DPD colorimetric method is most common. Follow the reagent manufacturer's instructions exactly; timing affects the result.
- Dissolved oxygen (DO) – Membrane electrode or optical probe. Calibrate according to manufacturer instructions; record water temperature alongside DO.
- BOD setup and incubation – Dilute sample, measure initial DO, incubate at 20 °C for five days, measure final DO.
Record every result on the bench sheet immediately—never from memory later. Note the instrument ID and calibration date. Compare results to permit limits or process targets and note any value that requires follow-up. If a result seems out of range, re-check calibration, re-run the test if holding time allows, and notify your supervisor.
Safety in the Lab and at Sampling Points
- Wear the PPE required for each task: safety glasses, nitrile gloves, and a lab coat or coveralls for chemical handling; steel-toed boots and a hard hat at outdoor sampling points.
- Acids and bases used for preservation are corrosive. Keep the SDS accessible. Never add water to concentrated acid—add acid to water.
- Biological samples (coliform, wastewater) are potential biohazards. Wash hands thoroughly after handling.
- Follow lockout/tagout (LOTO) procedures if accessing any sampling point that requires isolating energy—never reach into a confined space or near rotating equipment without following facility confined-space and LOTO protocols.
- Dispose of chemical waste from lab tests according to the facility's waste disposal SOP; never pour reagents down a drain without authorization.
Regulatory Operating Reports
Daily and monthly operating reports (also called discharge monitoring reports or DMRs at wastewater facilities) are official regulatory documents submitted to the state agency. Key rules:
- Copy directly from source data. Transcribe instrument readings, bench sheets, and lab reports—do not estimate or round beyond the number of significant figures your method supports.
- Fill every required field. A blank field is a critical error. If a measurement was not taken, note why (equipment down, no flow, etc.).
- Units must match the permit. mg/L is not the same as µg/L; MGD is not the same as gpd.
- Math must be correct. Check averages, totals, and unit conversions before signing.
- Supervisor review before filing. Your supervisor will provide written feedback; correct every noted error before the final version is filed.
Falsifying any entry on a regulatory report is a criminal offense under federal and most state laws. If you make an honest mistake, correct it promptly and transparently, following the facility's error-correction procedure.
Key terms10
Grab sampleA single sample collected at one location and one point in time, representing conditions at that specific moment.
Composite sampleA sample formed by combining multiple grab sub-samples collected over time or at multiple locations to represent average conditions.
Chain of custody (COC)A legal document that records every person who handles a sample from collection through analysis, ensuring sample integrity and providing evidence of proper handling.
Holding timeThe maximum allowable time between sample collection and laboratory analysis; exceeding it invalidates the sample result.
Sample preservationTechniques—such as chilling, chemical addition, or light exclusion—used to prevent changes in sample composition between collection and analysis.
Discharge Monitoring Report (DMR)An official regulatory report submitted to the state agency documenting measured effluent or system parameters and comparing them to permit limits.
DPD colorimetric methodA widely used test procedure in which a reagent reacts with free or total chlorine to produce a color whose intensity is measured to determine chlorine residual concentration.
Nephelometric Turbidity Unit (NTU)The standard unit used to report turbidity as measured by a nephelometer, which quantifies light scattered by particles in a water sample.
Bench sheetA standardized data-recording form used in the plant laboratory to document instrument IDs, calibration, raw test results, and analyst information at the time of measurement.
Standard operating procedure (SOP)A written, step-by-step instruction that standardizes how a specific task—such as sampling or a laboratory test—is performed to ensure consistent, defensible results.
Worked examples4
1. A turbidimeter reading for filtered water is 0.42 NTU. The permit limit for filtered water turbidity is 0.3 NTU. Is the facility in compliance, and what should the operator do?
- Step 1: Compare the measured value to the permit limit. Permit limit = 0.3 NTU; measured value = 0.42 NTU.
- Step 2: Determine compliance status. 0.42 NTU > 0.3 NTU, so the result exceeds the permit limit.
- Step 3: Record the result exactly as measured on the bench sheet with instrument ID, calibration date, time, and analyst name.
- Step 4: Note 'EXCEEDS PERMIT LIMIT – notify supervisor immediately' in the required follow-up section of the bench sheet and in the field journal.
- Step 5: Do not alter or round the value to make it appear compliant. Notify the supervisor so the appropriate regulatory notification and corrective action can be initiated.
Answer: The facility is NOT in compliance (0.42 NTU exceeds the 0.3 NTU limit). The operator records the true value, flags it, and notifies the supervisor without delay.
2. You are setting up a five-day BOD test. You measure an initial DO of 8.6 mg/L in the diluted sample bottle. After five days at 20 °C, the final DO is 3.1 mg/L. The dilution factor is 20 (you used 5 mL of sample in a 100 mL bottle, then filled to 300 mL — net dilution = 300 mL ÷ 15 mL sample = 20). Calculate the five-day BOD.
- Step 1: Identify the formula. BOD₅ (mg/L) = (Initial DO – Final DO) × Dilution Factor.
- Step 2: Calculate the DO difference. 8.6 mg/L – 3.1 mg/L = 5.5 mg/L.
- Step 3: Apply the dilution factor. 5.5 mg/L × 20 = 110 mg/L.
- Step 4: Record the result with appropriate significant figures and units on the bench sheet.
Answer: BOD₅ = 110 mg/L
3. A monthly operating report requires the average daily flow for a seven-day period. The daily flow readings (in MGD) are: 1.82, 1.75, 1.90, 1.68, 1.85, 1.77, 1.80. Calculate the seven-day average daily flow.
- Step 1: Add all seven daily flow values. 1.82 + 1.75 + 1.90 + 1.68 + 1.85 + 1.77 + 1.80 = 12.57 MGD (total).
- Step 2: Divide the total by the number of days. 12.57 ÷ 7 = 1.7957... MGD.
- Step 3: Round to match the precision of the source data (two decimal places). Average = 1.80 MGD.
- Step 4: Enter 1.80 MGD in the correct field on the operating report, ensuring units (MGD) match the permit requirement.
Answer: Seven-day average daily flow = 1.80 MGD
4. You collect a grab sample for total coliform at 10:15 a.m. The required holding time for a coliform sample is 6 hours when preserved with sodium thiosulfate and chilled. At what time does the holding time expire, and what must you confirm before the sample leaves the site?
- Step 1: Calculate expiration time. 10:15 a.m. + 6 hours = 4:15 p.m.
- Step 2: Confirm the sterile container already contains the correct amount of sodium thiosulfate (pre-preserved by the lab) — do NOT rinse a sterile coliform container.
- Step 3: Place the sample immediately on ice in the cooler to maintain ≤6 °C.
- Step 4: Complete the chain-of-custody form: sample ID, location, collection time (10:15 a.m.), date, preservative (sodium thiosulfate — pre-added), required analysis (total coliform), and your signature.
- Step 5: Have the supervisor review and sign the COC before the sample leaves the site, ensuring it will reach the lab before 4:15 p.m.
Answer: Holding time expires at 4:15 p.m. The sample must reach the lab before that time, be kept on ice, and the completed COC must be reviewed by the supervisor before departure.
The math in this lesson1
Learners compare a 0.42 NTU turbidity result to a 0.3 NTU permit limit and record exceedance.
N-Q.3
In class: Collect grab and composite samples at assigned facility sampling points following standard methods for sample preservation, container type, and holding time; complete a chain-of-custody form for each sample set; present completed forms to the supervisor for review before samples leave the site. · Perform or directly assist with at least five different on-site laboratory tests (such as pH, turbidity, chlorine residual, dissolved oxygen, total coliform or BOD setup, as applicable), record results on the bench sheet, compare values to permit limits or process targets, and note any required follow-up actions in the field journal. · Complete at least two weeks of the facility's official daily or monthly operating reports under supervisor guidance, ensuring all required fields are filled, units are correct, and data matches source instrument readings; supervisor reviews each report and provides written feedback before the student files the corrected version.
Materials: Approved sample containers, coolers with ice, chain-of-custody forms, field parameter meters (pH meter, turbidimeter, colorimeter/comparator for chlorine residual, DO meter), bench data sheets, facility daily and monthly operating report forms, relevant state regulatory reporting guidance, student field journal
Check: Supervisor scores sampling and lab technique using the Sampling and Recordkeeping rubric; all chain-of-custody forms accepted without critical errors; operating report entries verified against source data with no arithmetic or transcription errors rated critical; overall rubric score satisfactory or above.
Practice check8
Answer each question, then check it. Nothing is recorded; this is your own practice.
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