Objective. Students will prepare and incubate BOD5 samples, filter and dry TSS samples, and measure settleable solids using an Imhoff cone, recording all data in the correct format and calculating final results in standard reporting units.
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Biochemical Oxygen Demand (BOD), Total Suspended Solids (TSS), and settleable solids are three of the most important measurements in wastewater treatment. Regulatory agencies use them to set permit limits, operators use them to judge plant performance, and licensing exams test them heavily. Understanding how to collect, prepare, and analyze samples correctly — and how to record results in standard units — is a core competency for any Class I or Class II wastewater operator.
BOD measures the amount of dissolved oxygen that microorganisms consume while breaking down organic matter in a water sample over five days at 20°C. The subscript "5" refers to the five-day incubation period, which is the standard test duration. A high BOD reading means a lot of organic material is present; a low reading means the water is cleaner. Wastewater treatment plants are designed to reduce BOD before discharge.
Sample preparation. Raw wastewater contains far too much organic material for a direct measurement — the bottle would run out of oxygen before five days are up. You must dilute the sample with dilution water: aerated, clean water that has been saturated with dissolved oxygen. Dilution water is sometimes "seeded" with a small volume of treated effluent or a commercial seed preparation to ensure enough active bacteria are present to perform the biodegradation. Choose a dilution ratio so that the final dissolved oxygen (DO) at day 5 is at least 1 mg/L but no more than 7 mg/L has been consumed; this ensures the test is valid.
Procedure. Fill duplicate 300 mL BOD bottles completely (no air space) with your diluted sample. Measure and record the initial DO (DO_i) with a calibrated DO meter immediately after filling. Seal the bottles and place them in a 20°C incubator. After exactly five days, remove the bottles, measure final DO (DO_f), and record. Calculate BOD5 using the standard formula:
> BOD5 (mg/L) = (DO_i − DO_f) × Dilution Factor
The dilution factor equals the total bottle volume divided by the volume of sample added (e.g., if you added 6 mL of sample to 294 mL of dilution water to fill a 300 mL bottle, the dilution factor is 300/6 = 50).
Safety. Wastewater is a biohazard. Wear nitrile gloves, safety glasses, and a lab coat at all times. Wash hands thoroughly after handling samples. Dispose of wastewater samples according to your facility's standard operating procedures.
TSS is the mass of solid material retained on a glass fiber filter after a measured volume of sample is passed through it under vacuum. Results are reported in milligrams per liter (mg/L). TSS is a direct measure of particulate matter in the water and is a standard permit parameter for wastewater effluent.
Procedure. Pre-weigh a glass fiber filter (Whatman GF/C or equivalent) on an analytical balance after it has been dried and cooled in a desiccator; record this as the tare weight (W1). Assemble the vacuum filtration unit, place the filter, and filter a measured volume of well-mixed sample — typically 100 mL, though you may adjust for solids-rich samples. Transfer the filter to a drying oven and dry at the temperature and duration specified in the approved method (commonly around 103–105°C for at least one hour). Cool the filter in a desiccator to room temperature, then reweigh it and record as W2.
Calculation:
> TSS (mg/L) = [(W2 − W1) in mg] ÷ Volume filtered in liters
Record all weights to at least four decimal places on the balance (0.1 mg readability). Label your filters clearly. Duplicate or triplicate samples improve reliability.
Safety. The drying oven is hot; use heat-resistant gloves when handling filters. Do not use the desiccator while it contains solvents. Confirm the desiccant (usually silica gel) is still active (blue, not pink, for indicating silica gel).
Settleable solids are the portion of suspended material that will gravity-settle from one liter of sample in 45 minutes. The Imhoff cone is the standard apparatus: a graduated, cone-shaped glass or plastic vessel marked in milliliters. Results are reported in mL/L.
Procedure. Pour a well-mixed, 1-liter sample into the Imhoff cone. Allow it to settle undisturbed for 40 minutes. At 40 minutes, gently stir or rotate the cone walls with a glass rod to dislodge material clinging to the sides; then allow to settle for an additional 5 minutes (45 minutes total elapsed time). Read and record the volume of settled material at the bottom of the cone in mL/L.
This test is fast, simple, and requires no electricity or chemicals. Many industrial and municipal pretreatment permits specify settleable solids limits. A result above the permit limit signals a problem upstream in treatment or in the industrial discharge feeding the plant.
All raw data — weights, volumes, DO readings, times, temperature, instrument calibration records — must be entered directly into your lab notebook in ink at the time of measurement. Never record on scratch paper and transcribe later. Initial and date each page. Include units on every value. These practices are required by Standard Methods and by state regulatory agencies when reviewing lab records.
State Class I and Class II wastewater operator exams include questions on BOD calculation, TSS methodology, and interpretation of settleable solids results. You must know the formula, the correct units, and what a high or low result means for plant operations. Accurate sampling and documentation protect the public and protect your license.
Answer each question, then check it. Nothing is recorded; this is your own practice.
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