Overview of sandy shores and mud flats in intertidal ecosystems
Exposed beaches: Most organisms buried.
Protected sand flats: More organisms at the surface; higher diversity.
Few seaweeds; no sessile animals.
Wave action influences particle size and slope:
Heavy wave action: Coarse sediments – found on exposed beaches.
Little wave action: Fine sediments – found on sand flats (Nybakken & Bertness Fig. 6.38).
Coarse sand beaches: Drain well; dry quickly; host fewer organisms.
Fine sand beaches: Retain more water (capillary action); support more organisms; sediment suitable for burrowing.
Sand buffers against significant temperature and salinity changes.
Sand acts as a barrier against UV light and desiccation.
Oxygen availability may be limited in fine-grained sands.
Organisms may burrow deeper in intertidal zones (up to 50 cm).
Common adaptations include heavy shells and longer siphons for filter-feeding.
Faster burrowing observed in organisms on exposed beaches (Levinton Fig. 16.26).
Swash riding: Organisms periodically leave sediment, ride waves, and reburrow for feeding and refuge from predation (Levinton Fig. 16.9).
Example species: Emerita sp., Donax sp.
Limited primary producers
Exposed sand beaches: Mostly benthic diatoms.
Protected flats: Diverse diatoms, dinoflagellates, cyanobacteria often form surface film.
Dominant macrofauna: Bivalves, annelids, crustaceans; primarily suspension and detritus feeders, scavengers.
Meiofauna: Microscopic organisms in sediment (62 – 500 µm), include ciliates, flatworms, nematodes; serve as food for macrofauna (Levinton Fig. 15.4).
Zonation not clearly defined due to tidal migrations.
Supralittoral fringe: Burrowing scavengers (air-breathing crustaceans).
Midlittoral zone: Highly variable.
Infralittoral fringe (surf zone): Highest aquatic diversity.
Dominated by annelids (surface and burrowing deposit feeders).
Includes various amphipods, bivalves as surface burrowers and suspension feeders.
Predators include moon snails, whelks, crabs, birds, and fish.
Communities highly variable temporally and spatially due to predation and biological disturbances.
Many infaunal species in sand flats have opportunistic life history traits.
Significant impacts from predators through direct predation and habitat disturbance.
E.g., Moon snail (Polinices duplicatus) preys on soft-shelled clams while disturbing substrate, affecting other infauna.
Form in protected areas, fine-grained sediments accumulate organic matter.
Located in bays, lagoons, estuaries; more stable than sand substrates.
Often develop anaerobic conditions due to poor water exchange.
RPD: Zone of rapid chemical change.
Below RPD: Anaerobic conditions; organic compounds decomposed by anaerobic bacteria.
Above RPD: Aerobic decomposition; compounds oxidized.
Chemoautotrophic bacteria inhabit the RPD, contributing to primary production (Levinton Fig. 15.5, 15.6).
Organisms often have permanent/semi-permanent burrows, with visible openings.
Thinner shells are common as adaptations to anaerobic conditions.
Organisms utilize oxygenated surface water for respiration, often possessing hemoglobin or similar pigments.
Support various seaweeds, diatoms, and seagrasses; notable for substantial primary productivity.
Large microbial populations include heterotrophic bacteria and chemoautotrophic bacteria in RPD crucial for nutrient cycling and food sources.
Macrofauna similar to sand-dwelling species but generally larger and more abundant.
Most energy derived from detritus; abundant organic matter and productivity sustain food webs.
Dominant feeding types: deposit and suspension feeders consuming primarily detritus; few herbivores as plant matter quickly becomes detritus colonized by bacteria (Levinton Fig. 15.8).
Shorebirds exhibit varied migration patterns, morphology, and habitat specificity.
Examples include Ruddy Turnstone, Marbled Godwit, Northern Phalarope.
Wintering shorebirds have a significant impact on infaunal communities.
English mud flats: Shorebirds consume up to 90% of Hydrobia snail population and 80% of nereid annelids.
On the East Coast of the US, 50-70% of invertebrate populations are affected.
Recovery of invertebrate populations observed with seasonal bird migrations.