Standard 1000 mL Transparent Graduated Settlometer Cylinder
Wide-bore cylindrical vessel (1000 mL capacity, 10 mL subdivisions) minimizing wall friction artifacts.
Evaluate the settling velocity and compactibility of biological activated sludge, measure 30-minute settled sludge volume (SSV30) in a 1-L cylinder, and determine the Sludge Volume Index (SVI) according to Standard Methods 2710 D. Explore interactive structural mechanics, materials simulation, and civil engineering telemetry.
Ready to sample with MLSS Concentration = 2.5 g/L.
Adjust MLSS Concentration, then execute civil engineering measurement.
Civil engineering telemetry is evaluated rigorously using 64-bit IEEE 754 precision. Residuals reflect ordinary least-squares regression across successive observations. Continuous data structures support high-fidelity structural mechanics and geotechnical continuum modeling.
The civil engineering physical models apply within the specified calibrated operational window (1.5 to 4.0 g/L). Evaluated on healthy, well-flocculated municipal activated sludge mixed liquor. Linear regression correlates 30-minute settled sludge volume SSV30 directly to MLSS concentration with slope SVI = 95.0000 mL/g.
Wide-bore cylindrical vessel (1000 mL capacity, 10 mL subdivisions) minimizing wall friction artifacts.
Tracks sludge-liquid interface height at 1, 2, 5, 10, 15, 20, 25, and 30 minutes.
Ultra-slow paddle (1 to 2 rpm) preventing sludge bridging across vessel walls.
Examines activated sludge flocs at 100x–400x magnification to quantify filamentous bacteria presence.
Filters mixed liquor through Whatman 934-AH discs to determine dry biomass concentration (g/L).
Verifies mixed liquor sample maintains > 2.0 mg/L DO prior to settling test.
Evaluate the settling velocity and compactibility of biological activated sludge, measure 30-minute settled sludge volume (SSV30) in a 1-L cylinder, and determine the Sludge Volume Index (SVI) according to Standard Methods 2710 D. Standardized parameter settings: 1.5, 2.0, 2.5, 3.0, 3.5, 4.0 g/L.
Collect fresh mixed liquor from the aeration basin discharge; aerate gently during transport to prevent anoxic denitrification and rising sludge.
Filter a 50 mL aliquot through pre-weighed glass-fiber filter; dry at 105 °C to determine dry biomass concentration MLSS (g/L).
Prepare six 1000 mL settled cylinder samples across target MLSS concentrations (1.5, 2.0, 2.5, 3.0, 3.5, and 4.0 g/L) by dilution with clarifier supernatant.
Invert cylinder three times to homogenize flocs; place on level bench; start digital timer immediately; observe zone settling velocity.
Record the descending sludge-liquid interface elevation at 5-minute intervals; record final 30-minute settled volume SSV30 (mL/L).
Compute SVI = SSV30 / MLSS; prepare wet mount slide under phase-contrast microscope to examine floc architecture and filamentous organism abundance.
Points are your recorded observations. The solid regression line validates Sludge Volume Index (SVI) mathematical scaling.
| # | Mixed Liquor Suspended Solids Concentration (MLSS) (g/L) | 30-Min Settled Sludge Volume SSV30 (mL/L) | Mixed Liquor Suspended Solids MLSS (g/L) | 30-minute settled sludge volume SSV30 (mL/L) | Remove |
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No readings yet. Execute a civil engineering trial and record it.
In civil municipal environmental engineering, the activated sludge process is the primary secondary biological wastewater treatment technology worldwide. Heterotrophic bacterial flocs suspended in an aerated basin oxidize dissolved organic pollutants; the biological suspension (mixed liquor) then flows into secondary clarifiers where biological flocs must settle rapidly by gravity to produce a crystal-clear effluent and a concentrated return activated sludge (RAS) stream. Sludge settleability and compaction characteristics are standardized under Standard Methods 2710 D using the Sludge Volume Index (SVI). SVI is defined as the volume in milliliters occupied by 1.0 gram of activated sludge solids after 30 minutes of quiescent gravity settling in a 1000 mL graduated cylinder (or settlometer): SVI (mL/g) = [SSV30 (mL/L) · 1000] / [MLSS (mg/L)] = SSV30 (mL/L) / MLSS (g/L). An SVI between 80 and 120 mL/g signifies ideal, rapidly settling, dense biological flocs with a well-clarified supernatant. An SVI < 70 mL/g indicates dense 'pin-point' flocs that leave a turbid effluent; while an SVI > 150 mL/g signals catastrophic 'sludge bulking' caused by the excessive proliferation of filamentous bacteria (such as Microthrix parvicella or Sphaerotilus natans). Bulking sludge will not compact, overflowing clarifier weirs and contaminating receiving rivers. In this laboratory investigation, mixed liquor samples across MLSS concentrations from 1.5 to 4.0 g/L are tested in 1.0 L settlometers to calibrate the settling response and verify optimal SVI = 95.0 mL/g.
Evaluated on healthy, well-flocculated municipal activated sludge mixed liquor. Linear regression correlates 30-minute settled sludge volume SSV30 directly to MLSS concentration with slope SVI = 95.0000 mL/g.