Coral reefs are increasingly threatened by coastal development activities that elevate turbidity and resuspend sediment. This project, conducted by Texas A&M University-Corpus Christi (TAMUCC) in partnership with the Florida Department of Environmental Protection (DEP), evaluated the sublethal impacts of suspended sediments on Orbicella faveolata, a threatened and ESA-listed coral species particularly vulnerable to sediment stress and stony coral tissue loss disease (SCTLD).
Using controlled laboratory experiments, the study exposed O. faveolata fragments to suspended sediments collected from two sources: a natural reef (carbonate-dominated) and a port channel (fine-grained, contaminated). The experiments were conducted at two turbidity levels (4 and 15 NTU). Corals were assessed over 30 days for metabolic performance (via oxygen consumption), calcification (using total alkalinity anomaly), and photosynthetic efficiency (via PAM fluorometry). A subsequent recovery period was monitored to assess resilience following stressor exposure.
Key findings include:
• Sediment characterization revealed that port sediments had a higher organic content (66.2% vs. 24.0%) and elevated concentrations of heavy metals, including arsenic, copper, and zinc, as well as altered microbial communities with potential pathogenic risks.
• Sublethal physiological impacts were observed across treatments. Corals exhibited trends of reduced photosynthetic efficiency, protein concentration, and symbiont density—despite no visible bleaching—highlighting subtle but meaningful biological stress.
• Calcification and growth rates differed significantly across treatments. Surprisingly, corals exposed to port sediments exhibited higher net calcification in some cases, potentially due to a greater chlorophyll-to-symbiont ratio that supported photosynthesis despite turbidity stress.
• Respiration rates (oxygen consumption) fluctuated over time, indicating metabolic strain. Increased oxygen demand early in exposure may serve as a useful early-warning metric of coral stress.
• Recovery varied by genotype. Some corals failed to return to their pre-stress physiological conditions after five weeks, particularly those from genotypes that showed the most significant photophysiological decline during exposure.
Multivariate analyses revealed that sediment source and associated contaminants (especially heavy metals) were primary drivers of coral response, along with treatment turbidity and coral genotype. While direct mortality was not observed, the cumulative effects of reduced metabolic and photobiological function indicate potential long-term vulnerability under repeated exposure scenarios. These findings provide critical evidence to inform DEP and other regulatory agencies in updating water quality criteria and sediment management practices. The study supports the implementation of sublethal physiological endpoints (e.g., respiration, protein loss, and photosynthetic decline) into environmental permitting and coral reef impact assessments. It also emphasizes the need for stricter turbidity thresholds and post-disturbance monitoring during and after coastal construction activities. In summary, this work advances our understanding of how viii chronic, moderate turbidity affects coral health, identifies key sediment-related risk factors, and highlights the importance of incorporating sensitive physiological metrics into coral reef conservation and resilience planning.
The content on the Florida Department of Environmental Protection's (DEP's) website was written and published in English, and English is the sole authoritative language for all such content. As an aid to site visitors who might benefit from multiple language options, the website offers an automated translation feature for browser content in the footer. The translation link will not convert attached or linked files, such as PDFs.
The website translation feature uses Gtranslate® (https://www.drupal.org/project/gtranslate). Gtranslate® is a third-party tool which is not owned, maintained, modified, or controlled in any way by DEP, and which is not endorsed by DEP as preferable to either human-generated translations, or any other automated translation options.
Translation is a nuanced and complex activity and computer-generated translations cannot be expected to be perfectly accurate. Automated translations of this site are not reviewed in advance by DEP and could convey incorrect or offensive language. DEP disclaims any liability for errors, omissions, or interpretive inconsistencies arising in the context of such translation. Site users assume all risk in using translated text. DEP is not responsible for any loss, damage, or harm resulting from reliance on translated text. Use of the translation tool in this website implies understanding and agreement with this assumption and disclaimer.