Turbidity vs Total Suspended Solids (TSS) Relationship

TIME: 2026.02.18 AUTHOR: Coco Li NUMBER OF VIEWS 334
Turbidity vs Total Suspended Solids (TSS) Relationship | Complete Guide

Turbidity vs Total Suspended Solids (TSS) Relationship

Fundamental Understanding

Turbidity measures light scattering by suspended particles, while TSS measures the actual weight of those particles. They are related but not directly convertible - the relationship depends on particle characteristics, composition, and size distribution.

Core Definitions Comparison

Turbidity

Definition: Optical property that causes light to be scattered and absorbed rather than transmitted through water

Units: NTU (Nephelometric Turbidity Units), FNU, FTU

Measurement: Optical instrument (nephelometer)

Key Feature: Measures light scattering effect

Total Suspended Solids (TSS)

Definition: Dry-weight of particles retained on a filter of specified pore size

Units: mg/L, g/m³

Measurement: Gravimetric analysis (filtering, drying, weighing)

Key Feature: Measures actual particle mass

The Correlation Relationship

The relationship between turbidity and TSS is not linear but follows a general correlation that varies based on water source and particle characteristics.


Factors Affecting Correlation

Particle Size

Smaller particles scatter more light per unit mass, increasing turbidity relative to TSS.

High Impact
Particle Shape

Irregular shapes scatter light differently than spherical particles.

Medium Impact
Particle Color

Dark particles absorb more light, reducing turbidity readings.

Medium Impact
Particle Composition

Clay vs. organic matter vs. algae - each has different optical properties.

High Impact
Critical Consideration

Never assume a fixed conversion factor between turbidity and TSS. Site-specific correlation must be established through parallel measurements. Using generic conversion factors can lead to errors up to 300%.

Conversion Formulas & Guidelines

General Conversion Formula

TSS (mg/L) ≈ k × Turbidity (NTU)

Where k is the correlation factor that must be determined empirically for each water source.

Typical Correlation Factors by Water Type

Typical Correlation Factors by Water Type

Water Type Typical k Factor Range R² Value Reliability
Drinking Water 0.8 - 1.2 0.6 - 1.5 0.85 - 0.95 High
River Water 1.5 - 2.5 1.0 - 4.0 0.70 - 0.85 Medium
Lake Water 1.2 - 2.0 0.8 - 3.0 0.65 - 0.80 Medium
Wastewater 2.0 - 3.5 1.5 - 5.0 0.60 - 0.75 Low
Stormwater 2.5 - 4.0 2.0 - 6.0 0.55 - 0.70 Low

Measurement Method Comparison

Aspect Turbidity Measurement TSS Measurement
Time Required Seconds to minutes Hours (filtering + drying)
Cost per Sample Low ($1-5) High ($20-50)
Equipment Needed Turbidimeter Filters, oven, balance, glassware
Real-time Capability Yes (continuous monitoring) No (laboratory analysis)
Regulatory Acceptance For process control For compliance reporting
Operator Skill Low to moderate High (trained technician)

Best Practices for Correlation

  1. Parallel Sampling: Collect turbidity and TSS samples simultaneously
  2. Adequate Data Points: Minimum 20-30 paired measurements for reliable correlation
  3. Seasonal Variation: Establish correlations for different seasons
  4. Flow Conditions: Account for high vs low flow periods
  5. Statistical Analysis: Use linear regression with R² > 0.7 for acceptance
  6. Regular Re-evaluation: Update correlation annually or when conditions change
Turbidity Measurement Total Suspended Solids Correlation Analysis Conversion Factors Water Quality Laboratory Analysis Particle Size Statistical Correlation

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