Field-trip logistics
Hamilton students: meet at Gate 9 for the bus (both the Bowen and Mt Maunganui legs).
Tauranga students (Rocky-shore trip): new start time 12 PM Sunday (low tide occurs 14{:}40, giving better exposure).
Quiz 1 deadline extended because of an IT outage
Original cut-off: Tuesday night.
New cut-off: Wednesday 11 : 30 AM.
Introduce soft-sediment (off-shore) ecosystems.
Examine their biogeochemistry and the ecosystem services they provide.
Lay physical foundations today; Lectures 7 & 8 will focus on organic–sediment interactions and the two dominant feeding modes.
Cover ≈ 90 % of the seafloor.
Habitable space is 3-D (surface + sub-surface) → high biodiversity & high organismal density.
Sediment is mobile (waves, currents) → habitats are dynamic.
Critical to: fisheries (cockles, mussels, nursery grounds), pollution monitoring (bio-indicator species), carbon sequestration, and benthic–pelagic coupling.
Support > 17 phyla + tens-of-thousands of foraminiferan species.
Example density: nematodes up to 4.5 × 10⁶ ind m⁻².
Many organisms tiny/cryptic → true richness likely underestimated (deep-sea sampling challenges).
Epifauna – live on sediment surface (e.g., scallops). Easy to census via divers or drop-cams.
Infauna – live within sediment (e.g., Arenicola lugworms). Require coring + sieving.
Surface clues: feeding pockets, waste piles, ventilation holes.
Interstitial fauna – microscopic animals inhabiting voids between grains (copepod nauplii, tardigrades etc.).
Megabenthos > few cm (stingrays, rays).
Macrofauna > 500\,\mu\text{m} (cockles, polychaetes, sponges).
Often act as bioturbators (sediment mixing, bio-irrigation → deeper O₂ penetration).
Meiofauna 63–500 \mum (nematodes, harpacticoid copepods).
Microfauna < 63 \mum (bacteria, archaea).
Consume organic-coated sediment particles.
Surface example: Hobsonia (polychaete) uses cilia to sweep across grains.
Sub-surface example: Macoma/Macomona (bivalve)
Extends inhalant siphon to surface → draws down particles → sorts OM on gills → ejects inorganic waste as surface pseudofaeces.
Arenicola marina (lugworm)
Creates a feeding pocket which it fluidises.
Can process several times its body weight daily, dragging O₂-rich water centimetres below the interface.
Capture particles from the water column.
Passive: parchment worm sits in a U-shaped tube; ambient currents deliver food to its mucus nets.
Active: mussels beat cilia → generate an inhalant current; organic particles captured on gills, non-nutritive material expelled as pseudofaeces.
First-order habitat control.
Coarse, sandy, well-sorted → higher energy → suspension feeders dominate.
Fine, muddy, poorly-sorted → low energy → deposit feeders dominate.
Measuring methods
Stack of sieves (traditional, cheap).
Laser diffraction (high-resolution, costly).
Sorting coefficient (after Folk & Ward 1957) \sigma\phi = \frac{\phi{84} - \phi{16}}{4} + \frac{\phi{95} - \phi_{5}}{6.6}
\sigma\phi \approx 1 ⇒ well sorted; \sigma\phi \ll 1 ⇒ poorly sorted.
Coarser grains behave intuitively: larger grain ⇒ larger critical shear stress.
Clays & silts defy expectations: despite small size they demand higher stress because
Electrostatic attractions bind particles.
Smooth grain faces offer little bed friction.
Thin layer above seabed where flow slows logarithmically.
Four sub-zones
Outer (free-stream, fastest).
Log layer (turbulent mixing; velocity drops \propto \log(z)).
Viscous–sublayer (weak turbulence + molecular diffusion).
Laminar diffusive film right at surface (almost no flow).
BBL thickness shrinks under high current velocity ⇒ rapid mass transfer; grows (up to \sim10 m) in deep, quiescent basins ⇒ diffusion-limited exchange.
Tank dye experiments show laminar streaking (low flow) vs turbulent dispersion (high flow).
Coarse sand → large pores → O₂ penetrates centimetres.
Fine mud → tight packing → O₂ exhausted after millimetres.
Transition zone is the RPD layer (Redox Potential Discontinuity).
Sharp vertical redox gradient is among the world’s steepest.
Aerobic surface ⇒ efficient OM oxidation:
\text{CHO}2 + O2 \rightarrow CO2 + H2O + \text{energy}
With depth, electron acceptors change → energy yield declines:
Nitrate reducers ⇒ sulfate reducers ⇒ methanogens.
Aerobic metabolism produces far more ATP than anaerobic pathways (oxygen a superior terminal electron acceptor).
In-situ autotrophs
Microphytobenthos (diatom films – visible green sheen on tidal flats).
Chemotrophic bacteria (use reduced compounds, no light).
Allochthonous supply dominates: phytoplankton fallout from the euphotic zone.
Continental shelf (0–200 m)
Area: 7.6 % of ocean but produces ≈ 82.6 % of benthic biomass (nutrient-rich, short transit time).
Abyssal plain (> 3 000 m)
Area: 77.1 % yet only 0.8 % of benthic biomass (nutrient poor + long particle transit allowing bacterial degradation en route).
Winter mini-bloom → slight rise in benthic metabolism.
Spring bloom → sharp benthic response.
Summer mega-bloom → intense benthic demand; risk of temporary anoxia from OM overload.
Demonstrates tight temporal linkage between surface productivity and seafloor processes.
Nitrogen is often limiting offshore, yet human loading (fertiliser, wastewater) delivers excess \text{N}.
Healthy sediments detoxify via coupled nitrification–denitrification:
Mineralisation: OM → \text{NH}_4^+ (ammonium).
Nitrification (aerobic bacteria in oxic layer)
\text{NH}4^+ \xrightarrow{O2} \text{NO}2^- \xrightarrow{O2} \text{NO}_3^-
Denitrification (anaerobic bacteria in anoxic zone)
\text{NO}3^- \rightarrow NO \rightarrow N2O \rightarrow N_2 \uparrow
Requires BOTH oxic and anoxic microsites.
If the oxic film collapses (high OM, low mixing) → ammonium accumulates → plankton/algal blooms → hypoxia/crashes: a vicious eutrophication cycle.
Nutrient regeneration – maintains productivity without external fertilisation.
Carbon sequestration – burial and anoxic preservation of OM.
Fisheries support – nursery grounds for fin-fish; habitat for shellfish aquaculture.
Pollution indicators – presence/absence of sensitive taxa tracks heavy metals, organic toxins, or nutrient enrichment.
Climate links – sedimentary denitrification releases N_2, curbing reactive \text{N} in oceans.
Equipment/activities
Extract cores; record depth of oxic/anoxic transition.
Sieve (> 500 µm) to collect macrofauna; count & size individuals.
Note surface clues (mounds, burrow openings, pseudofaeces strings).
Measure grain size distribution; calculate sorting.
Observational aims
Confirm predicted fauna from surface evidence.
Relate macrofaunal density to grain size & hydrodynamic exposure.
Balancing nutrient inputs: moderate enrichment can enhance productivity; excess triggers harmful algal blooms & dead zones.
Conservation of bioturbators vital – large burrowers maintain O₂ penetration, supporting whole nutrient web.
Recognising the invisible majority (micro/meiobenthos) in EIA and fishery management plans.
Edgar & Barrett (soft-sediment biodiversity).
Tyler et al. (benthic boundary layer processes).
Hjulström (sediment transport thresholds).
Cury & Biatetz (benthic–pelagic coupling studies).
Position classes: Epifauna / Infauna / Interstitial.
Size classes: Mega / Macro / Meio / Micro.
Feeding modes: Deposit (surface/sub-surface) vs Suspension (passive/active).
First-order physical driver: grain size.
Key chemical feature: millimetre-scale O₂ gradient; need both aerobic & anaerobic bacteria.
Nitrogen pathway: \text{OM} \rightarrow NH4^+ \xrightarrow{O2} NO3^- \xrightarrow{anoxic} N2.
Service mantra: "bioturbation → oxygen → nitrification → denitrification → healthy coast".