OSX-2007: Suspended Particulate Matter (SPM)
📌 1. Introduction to SPM
SPM (Suspended Particulate Matter): Refers to fine particles suspended in the water column.
Includes both inorganic particles (e.g., clay, silt, sand) and organic particles (e.g., phytoplankton, zooplankton fragments, faecal pellets, detritus).
Often visualised via turbidity (water clarity/murkiness).
Terminology:
SPM (Suspended Particulate Matter)
SSC (Suspended Sediment Concentration)
TSS (Total Suspended Solids)
MSS (Mineral Suspended Solids)
Organic SPM (via loss on ignition)
💡 2. Why Is SPM Important?
A. Physical and Geochemical Roles
Sediment Transport: SPM is carried by tidal/wave currents and resettles elsewhere (important for harbour sedimentation).
Biogeochemical Fluxes: Moves nutrients and organic/inorganic materials through systems.
Pollutant Vector: Pollutants (e.g. heavy metals, microplastics) adhere to particle surfaces and are transported with SPM.
B. Light Attenuation & Primary Production
Scattering of light by particles increases light path, making photons more likely to be absorbed.
Decreases photosynthetically active radiation (PAR) → impacts phytoplankton, seagrass, kelp, and benthic algae productivity.
C. Food Source
Organic fraction of SPM provides food for filter feeders (e.g. deep-sea sponges, corals, suspension feeders).
Marine snow = visible aggregates (flocs) of organic/inorganic material.
🧪 3. SPM Types and Dynamics
A. Simple Suspensions
Dominant in high-energy environments (e.g. near sandy seabeds).
Higher flows = resuspension of coarser particles (sands, silts).
B. Flocs (Aggregates)
Found in quiescent areas (low-energy), often during spring blooms.
Composed of:
Mineral particles (clay, silt)
Organic material (algae, faeces)
Entrained water
Turbulence:
Low: Allows growth of large flocs.
High: Breaks flocs apart into smaller particles.
Controlled by Kolmogorov length scale: the smallest eddies in a turbulent flow constrain floc size.
🌊 4. Spatial and Temporal Variability in SPM
A. Vertical (Depth) Variation
Higher SPM near the seabed due to gravity settling and turbulence from bed shear.
Larger particles settle faster, but strong bottom shear can resuspend them.
B. Horizontal Variation
Influenced by:
Tides: Strong tides = more SPM (especially in estuaries).
Wind/wave action: Storms = temporary SPM spikes.
Seabed type: Sandy vs. muddy vs. rocky.
Biological activity: Spring blooms increase organic floc formation.
C. Temporal Variation
Tides (semi-diurnal, spring-neap cycles) influence regular SPM cycling.
Storms cause episodic resuspension.
Horizontal advection: Movement of sediment plumes across measuring stations causes periodic variation.
📊 5. Measuring SPM in the Field
A. Gravimetric Analysis (Gold Standard)
Collect samples with Niskin bottles (surface and near-bed).
Filter water through pre-weighed filter papers.
Dry and re-weigh filters to determine mass of SPM.
SPM concentration = mass of particles / volume of water.
Loss on ignition can determine organic vs. mineral fractions (burning off organic material at ~500–550°C).
B. Optical & Indirect Methods
Instrument | Principle | Output |
|---|---|---|
Secchi Disk | Visibility depth | Clarity (inverse SPM) |
Transmissometer | Measures reduction in light beam | Light transmission (↓ = ↑ SPM) |
Optical Backscatter Sensor (OBS) | Infrared light scattering back to sensor | Voltage → SPM (via calibration) |
Satellite Imagery | Ocean colour algorithms estimate SPM | Surface concentration only |
Satellite Limitations: Only detects surface layers (top 10 cm – 2 m); requires cloud-free conditions.
📈 6. Modelling SPM Concentrations
A. Suspension-Settling Equilibrium
Turbulence resuspends particles.
Settling velocity (∝ particle diameter²) pulls them down.
Result: Exponential SPM decay profile from seabed upward.
B. Rouse Profile:
Predicts vertical SPM profile from particle size and turbulence.
Fine particles → well-mixed in water column.
Coarse particles → confined to near-bed zone.
C. Bed Shear Stress & Particle Mobilisation
Tides and waves generate bed shear stress (τ₀).
Different particles require different threshold τ₀ to be mobilised.
Shields Parameter used to estimate this critical τ₀.
D. % Time Above Threshold
Mapping the % of the year when τ₀ exceeds critical value shows areas of frequent sediment resuspension.
🧠 7. Twin-Peak Pattern in Time Series Data
Observed in beam transmittance data.
Caused by:
Advection of horizontal SPM gradient (semi-diurnal).
Vertical resuspension cycle (quarter-diurnal).
Combined effect creates double peaks per tidal cycle.
Example: Observed by Alison Weeks in the 1990s, described via sketches and models of combined advection-resuspension cycles.
🛰 8. Satellite & Model Data
Satellite:
High-resolution ocean colour imagery (e.g. MERIS).
Shows spatial patterns of surface SPM (e.g. turbid estuaries, tidal mixing zones).
Useful for large-scale patterns but limited to surface only.
Numerical Models:
Can simulate:
Bed shear stress from tides/waves.
Advection & resuspension patterns.
Example: Ratio of wave:tide bed shear reveals dominant process by region (e.g. tide-dominated Irish Sea vs. wave-dominated Dogger Bank).
🧾 9. Summary: Key Takeaways
SPM affects light, productivity, sediment transport, pollution, and food webs.
Controlled by physical (tides, waves, shear, turbulence) and biological (phytoplankton, flocculation) processes.
Varies spatially and temporally — driven by dynamic interactions.
Measurement techniques range from direct gravimetric sampling to indirect optical methods and satellite imagery.
Floc formation and break-up are turbulence-dependent; turbulence both controls and is influenced by SPM.
Tidal cycles and advective gradients generate distinctive twin-peak signals in SPM data.