The Effects of Upwelling on Hermatypic Coral Reefs by Mikayla Taylor
Introduction
The
process of upwelling is essentially a natural cooling system for the surface of
the world’s oceans. It is defined as the rising of deep, cold, nutrient rich
waters to the surface as wind pushes warmer surface waters offshore (NOAA 2024).
The changes in temperature and nutrient content brought about by this process
can be both beneficial and detrimental to marine ecosystems.
Graphic
demonstrating the replacement of windblown surface waters by colder,
nutrient-rich waters from below. (NOAA 2024)
One
crucial ecosystem affected by upwelling is coral reefs, more specifically
hermatypic (reef-building) corals. These species require very specific
temperature, pH, and turbidity conditions to survive and become highly
susceptible to life-threatening stress if oceanic conditions are outside of
their preferences even slightly. Their ideal temperature range is between 23-29°C (though this varies slightly
among species) (NOAA 2024), their ideal pH range is between 8.0-8.3 (the
standard pH of seawater) (Living Oceans Foundation n.d), and they require very
clear waters with maximum light penetration (low turbidity) (NOAA 2024). Outside
of these conditions, corals are at risk of losing their symbiotic algae called
Zooxanthellae that are their main source of energy through photosynthesis. This
is because the zooxanthellae become stressed and begin releasing a harmful
chemical that can damage the host coral’s tissues, so they expel the algae and
become bleached and vulnerable to disease (NOAA n.d.). These unideal parameters
also create a lack of the calcium carbonate (CaCO3) ions required to
build their hard exoskeletons due to higher dissolution rates and a reduced
ability to perform photosynthesis caused by inadequate sunlight.
As
shown by numerous studies, upwelling can provide support and reprieve for reefs
in a variety of ways but also worsen matters depending on case-to-case
variation.
The
Benefits of Upwelling
The
highest threat to coral reefs today is climate change, with warming sea surface
temperatures (SSTs) causing coral bleaching and reef health decline. Since
upwelling brings cooler water from the depths to the surface, it aids in
keeping bleaching events at bay. In regions like the Quiong Dong Upwelling Zone
(QDU) in the South China Sea where upwelling is a regular seasonal occurrence, SSTs
remain safe for corals even in the peak summer months, staying around 27°C and significantly preventing
bleaching when its most necessary. On the other hand, nearby non-upwelling
regions reach 31°C
and bleaching is much higher, especially in the hottest months of the year (Zhu
et al. 2022).
This
cooling ability is especially valuable during extreme climate events like the
El Nino Southern Oscillation (ENSO), when SSTs warm 0.5°C or more for months during the El
Nino phase causing mass global bleaching events (NOAA 2016; Claar et al. 2018).
During the 1997-98 El Nino, upwelling kept the Gulf of Panama below 30°C and prevented any bleaching,
while the non-upwelling zone of the Gulf of Chiriqui experienced a mass
bleaching after temperatures rose above 30°C
(D’Croz et al. 2001). Upwelling has shown to decrease the frequency, duration,
and severity of thermal disturbances by 55%, 24% and 4% respectively (Chollett
et al. 2010).
Map
of the Pacific demonstrating the SST differences between the upwelling Gulf of
Panama and non-upwelling Gulf of Chiriqui. (Gravinese et al. 2018)
Upwelling
also protects corals from fast, thick growing turf and macroalgae that may
compete with them for resources or smother them. Cooler water temperatures have
been shown to reduce the metabolic activity of these organisms. In the Pacific,
before the seasonal upwelling period, turf algae were found to have the highest
primary productivity rates on the reef, but as the upwelling season progresses,
their primary productivity remained stagnant as coral primary productivity
skyrocketed. Corals were shown to have made the largest contribution to reef
productivity by the end of the upwelling period (Stuhldreier et al. 2015).
For
already stressed or bleached corals, aid lies in the increased phytoplankton
density created by the upwelling of more nutrients. Since a lack of
zooxanthellae means decreased photosynthesis capabilities, corals can rely on
suspension feeding while bleached and the phytoplankton become a critical food
source (Sawall et al. 2020). Increased turbidity from higher phytoplankton
density also shields corals from excess UV rays that could increase their
stress, aiding in their recovery after bleaching events (Chollett et al. 2010).
Upwelling
as a Tool for Climate Mitigation
The
thermal refugia provided by upwelling is being mimicked through artificial
upwelling (AU), where scientists have been testing the effect of short pulses
of cool water from different ocean depths on different corals species in a
controlled laboratory environment or through simulation technology. Corals
exposed to AU exhibited significant indicators of improved health such as
increased photosynthesis rates, zooxanthellae density, and chlorophyll-a levels.
Less than two hours a day of upwelling conditions decreased the overall period
of thermal stress experienced by 1.6°C-weeks
(Sawall et al. 2020).
Coral
tank system used in Sawall et al. 2020 AU experiment. (Coxworth 2020)
Simulations
show AU reducing and delaying bleaching events for decades, but there are risks
to the method. Downwelling began to occur at the AU site, which warmed the deep
waters and reduced the temperature gradient that drives upwelling, therefore
weakening its cooling effect. Overly extreme AU practices can overcool surface
waters, increase surface acidity, and cause an excess nutrient influx. Ocean
circulation patterns can even be disrupted causing changes in ocean chemistry
and heat budget (Feng et al. 2020). For these reasons, AU requires further
research before we can utilize it in our fight to save the reefs.
The
Disadvantages of Upwelling and Stipulations of its Abilities
The
drawbacks of upwelling are usually scenario dependent. Non-stressed corals are
harmed by increased nutrients rather than helped because increased
phytoplankton density decreases their light availability (which is needed in
high amounts for photosynthesis), increased algae growth smothers them, and
harmful microbes can grow supported by the organic matter release of dying
phytoplankton (Sawall et al. 2020).
Dead
coral smothered by overgrown algae. (Wolcott 2010)
Upwelling
can cause an imbalance in nutrients like nitrogen and phosphate. When nitrogen
is high, but phosphate is limited, coral growth rate is higher but unsupported
by the necessary nutrients for cell maintenance, adding to coral stress
(Buckingham et al. 2022).
Corals
may be harmed simply by naturally living in an upwelling region and being
accustomed to it. In one study, corals from the Gulf of Panama (upwelling zone)
bleached faster and more severely when exposed to heat compared to Gulf of
Chiriqui (non-upwelling) corals, likely because they were already adapted to
the cooler temperatures in the area (D’Croz et al. 2001). This lack of
tolerance could cause a disaster in the face of an extreme climate event or an
interruption in the natural upwelling process.
Geographical
variability in upwelling makes it an inconsistent thermal refuge. During the 1982-83
ENSO, upwelling failed to cool waters enough to prevent bleaching in Panama –
both upwelling and non-upwelling zones had equal SSTs and bleaching, with coral
mortality even reaching almost 85% in the upwelling zone. Upwelling only works
as a thermal refuge when it occurs at the same time as warming seasons and has
a significant effect on SSTs, but this overlap can be hard to accomplish in
oceans like the Pacific where extreme thermal events often occur throughout the
entire year. In these regions, upwelling delays the warming period but doesn’t
reduce its length or severity (Chollett et al. 2010).
Considerations
of Anthropogenic Influence
It
is important to consider how human activity plays a role in the effects of
upwelling. Our greenhouse gas emissions have caused global warming and pollution
from coastal development and agricultural runoff contribute to excess nutrients
and competitive organism overgrowth. In Zhu et al. 2022’s study, land use
overshadowed the effects of upwelling because nutrient content was extremely
elevated. Results that were unusual for an upwelling zone were produced, like
lower turbidity and less acidic water (as compared to the non-upwelling zone),
showing that nearby anthropogenic influences disrupted the data. So, not only
does human activity cause the factors that stress corals, but it also prevents
us from properly measuring the impact we have, and which reefs need the most
help. Moving forward, we must work to alleviate the stressors we have the most
control over (like pollution) to give corals their best fighting chance and to
gain clearer understanding of how we can work alongside upwelling rather than
against it.
Conclusion
and Recommendations
Upwelling,
as both a natural and artificial process, shows great promise in providing
refuge for corals from detrimental climate changes by cooling SSTs, increasing
food supply, reducing UV radiation, and preventing overgrowth of other
competitive organisms. However, its success is highly dependent on seasonality,
location, and anthropogenic activity. To make the most of this potential
refugia, future studies should explore AU techniques more representative of natural
upwelling by introducing longer cooling periods rather than short bursts to
determine which duration of upwelling produces greater coral health over time. It
is important to critically analyze our unsustainable practices as humans as
well to be the better advocates for reef survival, especially as global warming
and extreme climate events continue to worsen. As time goes on and climate changes
worsens, it becomes more critical than ever that we analyze our unsustainable
practices to be better advocates and protectors of our beloved coral reefs!
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