Abstract
River runoff and associated flood plumes (hereafter river plumes) are a major source of land-sourced contaminants to the marine environment, and are a significant threat to coastal and marine ecosystems worldwide. Remote sensing monitoring products have been developed to map the spatial extent, composition and frequency of occurrence of river plumes in the Great Barrier Reef (GBR), Australia. There is, however, a need to incorporate these monitoring products into Risk Assessment Frameworks as management decision tools. A simple Satellite Risk Framework has been recently proposed to generate maps of potential risk to seagrass and coral reef ecosystems in the GBR focusing on the Austral tropical wet season. This framework was based on a “magnitude × likelihood” risk management approach and GBR plume water types mapped from satellite imagery. The GBR plume water types (so called “Primary” for the inshore plume waters, “Secondary” for the midshelf-plume waters and “Tertiary” for the offshore plume waters) represent distinct concentrations and combinations of land-sourced and marine contaminants. The current study aimed to test and refine the methods of the Satellite Risk Framework. It compared predicted pollutant concentrations in plume water types (multi-annual average from 2005–2014) to published ecological thresholds, and combined this information with similarly long-term measures of seagrass and coral ecosystem health. The Satellite Risk Framework and newly-introduced multi-annual risk scores were successful in demonstrating where water conditions were, on average, correlated to adverse biological responses. Seagrass meadow abundance (multi-annual change in % cover) was negatively correlated to the multi-annual risk score at the site level (R2 = 0.47, p < 0.05). Relationships between multi-annual risk scores and multi-annual changes in proportional macroalgae cover (as an index for coral reef health) were more complex (R2 = 0.04, p > 0.05), though reefs incurring higher risk scores showed relatively higher proportional macroalgae cover. Multi-annual risk score thresholds associated with loss of seagrass cover were defined, with lower risk scores (≤0.2) associated with a gain or little loss in seagrass cover (gain/−12%), medium risk scores (0.2–0.4) associated with moderate loss (−12/−30%) and higher risk scores (>0.4) with the greatest loss in cover (>−30%). These thresholds were used to generate an intermediate river plume risk map specifically for seagrass meadows of the GBR. An intermediate river plume risk map for coral reefs was also developed by considering a multi-annual risk score threshold of 0.2—above which a higher proportion of macroalgae within the algal communities can be expected. These findings contribute to a long-term and adaptive approach to set relevant risk framework and thresholds for adverse biological responses in the GBR. The ecological thresholds and risk scores used in this study will be refined and validated through ongoing monitoring and assessment. As uncertainties are reduced, these risk metrics will provide important information for the development of strategies to manage water quality and ecosystem health.
Highlights
The rapid development of coastal areas has resulted in a substantial increase in land-sourced contaminants entering the marine environment [1,2,3], with a “contaminant” defined in this study as “a substance that occurs at above ‘natural’ concentrations” [3]
We considered the proportion of the total cover of algae on a reef that is comprised of macroalgae, as opposed to the cover of macroalgae per se, as this allows the standardisation of macroalgae cover for space occupied by corals, loose sediments and other reef biota
This study contributes to the development, test and validation of innovative remote sensing monitoring tools currently undertaken in the Great Barrier Reef (GBR) in order to understand the relationships between pressures from human activities, including influences on coastal water quality, and their effects on marine ecosystems [15]
Summary
The rapid development of coastal areas has resulted in a substantial increase in land-sourced contaminants entering the marine environment [1,2,3], with a “contaminant” defined in this study as “a substance that occurs at above ‘natural’ concentrations” [3]. Identifying the movement, duration, frequency and composition of river plumes and associated coastal water quality is critical in measuring the exposure and risk to marine ecosystems of land-sourced contaminants. Marine Park (hereafter GBR; Figure 1) was inscribed on the World Heritage List in October, 1981 It is the most extensive reef system in the world, and shelters over 2900 coral reefs and 35,000 km of seagrass meadows [7,8]. The sediments, nutrients and herbicides discharged as agricultural runoff through river plumes have been identified as the contaminants of greatest concern with regards to their potential impacts on GBR key ecosystems, including coral reefs and seagrass meadows (e.g., [9,10]). Each plume water type is associated with characteristic optical properties, light levels and colours, as well as different concentrations and proportions of land-sourced contaminants (e.g., [11,12,13,14,15,16])
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