Coating matters in the invisible sea: Biofilms, marine snow and bioengineering
September 2, 2004 | 12:00am
In February 2002, after many months of dry and sunny weather, people in the province of Pangasinan witnessed a massive fish kill of bangus being raised in pens and net cages in Bolinao. Masses of dead fish discharged into the open water were soon after washed ashore with incoming tides. With a second mass kill of wild fish and shell fish following on the next day, a considerable stretch of the shoreline was to remain for weeks without the living resources which nutrient-rich intertidal flats are usually expected to sustain.
More recently, coastal marine waters, the everlasting domain of fish "hunters," is increasingly shared with fish "farmers." In economic terms, this makes sense, at least in theory. Could Philippine fish farmers eventually enjoy a similarly sustainable resource base as their cousins in the Ifugao Rice Terraces? Ecocatastrophic events like the one in Bolinao may provoke skepticism. On the other hand, large-scale fish farming has just begun, and we have to ask first: What do we really know about energy flow, carrying capacities, about Natures pathways of waste disposal and recycling? How can one reliably assess environmental risks?
Growing interest in food supply for ocean fisheries had paved the way for what later evolved as marine science. One of the early milestones in this development was the design of plankton nets to quantify all drifting organisms (plankton) that could be perceived as a source of fish feed. Defined mesh sizes were used to assess and predict fish production in the ocean. Sunlight-driven (photosynthetic) production of phyto-plankton biomass is mainly fueled by inorganic nutrients. As these become rapidly exhausted, their pools must always be replenished. This is achieved in half-cycles of remineralization that are linked with the formation of living biomass. According to early models, most of the dying plankton has to sink to the seafloor first. Here inorganic nutrients will be regenerated and eventually resurface to sunlight-exposed water layers to fuel another round of fish feed production. When the first models for oceanic ecosystems were applied several decades ago, they paradoxically predicted fish stocks would never be sustained due to lack of food, even under the most optimistic (but completely unrealistic) scenario that fish were able to consume 100 percent of the primary (photosynthetic) production. Apparently, these models were too simple. They relied only on the most visible organisms and their most evident functions.
Excess fish feed and feces undergoing "enzymatic burning" (respiration) with the help of dissolved molecular oxygen will rapidly deplete the dissolved oxygen in the water column, and even more so, at sediment surfaces on which sinking detritus particles are deposited. This does not mean, however, that recycling or remineralization of organic matter would have to stop, when dissolved oxygen pools have been exhausted. A sequence of alternative pathways replacing oxygen-dependant respiration will be at hand. In the sea environment, the most sustainable recycling pathway for organic matter under oxygen depletion depends on sulfate as an abundant component of seawater salts.
Organic matter recycling via this so-called "sulfate respiration" of marine microbes produces hydrogen sulfide, an easily recognized component with the smell of rotten eggs. Hydrogen sulfide (H2S) is toxic to most animals living in the sea, unless they can manage to produce detoxifying compounds binding it. Most importantly, this toxicant also binds heavy metals. By doing so, it helps to deposit and to detoxify another group of environmental toxicants. In oxygen-rich waters hydrogen sulfide will disappear rapidly. Therefore, clams, crabs and other sediment-inhabiting animals can survive in hydrogen sulfide-rich sediments so long as they manage to irrigate their surroundings with water containing oxygen. Only permanently high rates of hydrogen sulfide production will eventually erase sediment-inhabiting communities.
This scenario can be observed on the seafloor below excessively fed fish cages in Bolinao Bay (Pangasinan). Where hydrogen sulfide seeps out of the sediment and mixes with traces of oxygen in the water, a niche is created that attracts the filaments of hydrogen sulfide oxidizing bacteria. These giants in the world of microbes can create thick yellowish-white lawns covering the seafloor: the color stems from elemental sulfur, an oxidation product of hydrogen sulfide that is stored in the filaments. These sulfide-oxidizing microbial lawns initiate the restoration of the sediment as a residential area for bottom-living animals. As a "hot spot" of organic matter recycling, an ecologically sound seafloor is virtually perforated with the aerated burrows. Their biofilm-coated walls are housing the microbe-driven machinery of "biochemical "relais stations" as required for organic matter recycling. (To be concluded)
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