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Pausch RE, Hale JR, Kiffney P, Sanderson B, Azat S, Barnas K, Chesney WB, Cosentino‐Manning N, Ehinger S, Lowry D, Marx S. Review of ecological valuation and equivalency analysis methods for assessing temperate nearshore submerged aquatic vegetation. CONSERVATION BIOLOGY : THE JOURNAL OF THE SOCIETY FOR CONSERVATION BIOLOGY 2025; 39:e14380. [PMID: 39417608 PMCID: PMC11780217 DOI: 10.1111/cobi.14380] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 11/01/2023] [Revised: 06/03/2024] [Accepted: 06/08/2024] [Indexed: 10/19/2024]
Abstract
Nearshore seagrass, kelp, and other macroalgae beds (submerged aquatic vegetation [SAV]) are productive and important ecosystems. Mitigating anthropogenic impacts on these habitats requires tools to quantify their ecological value and the debits and credits of impact and mitigation. To summarize and clarify the state of SAV habitat quantification and available tools, we searched peer-reviewed literature and other agency documents for methods that either assigned ecological value to or calculated equivalencies between impact and mitigation in SAV. Out of 47 tools, there were 11 equivalency methods, 7 of which included a valuation component. The remaining valuation methods were most commonly designed for seagrasses and rocky intertidal macroalgae rather than canopy-forming kelps. Tools were often designed to address specific resource policies and associated habitat evaluation. Frequent categories of tools and methods included those associated with habitat equivalency analyses and those that scored habitats relative to reference or ideal conditions, including models designed for habitat suitability indices and the European Union's Water and Marine Framework Directives. Over 29 tool input metrics spanned 3 spatial scales of SAV: individual shoots or stipes, bed or site, and landscape or region. The most common metric used for both seagrasses and macroalgae was cover. Seagrass tools also often employed density measures, and some categories used measures of tissue content (e.g., carbon, nitrogen). Macroalgal tools for rocky intertidal habitats frequently included species richness or incorporated indicator species to assess habitat. We provide a flowchart for decision-makers to identify representative tools that may apply to their specific management needs.
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Affiliation(s)
- Rachel E. Pausch
- Department of Ecology and Evolutionary BiologyUniversity of California, Santa CruzSanta CruzCaliforniaUSA
| | - Jessica R. Hale
- National Marine Sanctuary FoundationSilver SpringMarylandUSA
- NOAA NWFSCSeattleWashingtonUSA
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Assessing Seagrass Restoration Actions through a Micro-Bathymetry Survey Approach (Italy, Mediterranean Sea). WATER 2022. [DOI: 10.3390/w14081285] [Citation(s) in RCA: 3] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [Abstract] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 02/05/2023]
Abstract
Underwater photogrammetry provides a means of generating high-resolution products such as dense point clouds, 3D models, and orthomosaics with centimetric scale resolutions. Underwater photogrammetric models can be used to monitor the growth and expansion of benthic communities, including the assessment of the conservation status of seagrass beds and their change over time (time lapse micro-bathymetry) with OBIA classifications (Object-Based Image Analysis). However, one of the most complex aspects of underwater photogrammetry is the accuracy of the 3D models for both the horizontal and vertical components used to estimate the surfaces and volumes of biomass. In this study, a photogrammetry-based micro-bathymetry approach was applied to monitor Posidonia oceanica restoration actions. A procedure for rectifying both the horizontal and vertical elevation data was developed using soundings from high-resolution multibeam bathymetry. Furthermore, a 3D trilateration technique was also tested to collect Ground Control Points (GCPs) together with reference scale bars, both used to estimate the accuracy of the models and orthomosaics. The root mean square error (RMSE) value obtained for the horizontal planimetric measurements was 0.05 m, while the RMSE value for the depth was 0.11 m. Underwater photogrammetry, if properly applied, can provide very high-resolution and accurate models for monitoring seagrass restoration actions for ecological recovery and can be useful for other research purposes in geological and environmental monitoring.
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Stockbridge J, Jones AR, Gaylard SG, Nelson MJ, Gillanders BM. Evaluation of a popular spatial cumulative impact assessment method for marine systems: A seagrass case study. THE SCIENCE OF THE TOTAL ENVIRONMENT 2021; 780:146401. [PMID: 33774293 DOI: 10.1016/j.scitotenv.2021.146401] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.3] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 11/29/2020] [Revised: 02/21/2021] [Accepted: 03/06/2021] [Indexed: 06/12/2023]
Abstract
Human activities put stress on our oceans and with a growing global population, the impact is increasing. Stressors rarely act in isolation, with the majority of marine areas being impacted by multiple, concurrent stressors. Marine spatial cumulative impact assessments attempt to estimate the collective impact of multiple stressors on marine environments. However, this is difficult given how stressors interact with one another, and the variable response of ecosystems. As a result, assumptions and generalisations are required when attempting to model cumulative impacts. One fundamental assumption of the most commonly applied, semi-quantitative cumulative impact assessment method is that a change in modelled cumulative impact is correlated with a change in ecosystem condition. However, this assumption has rarely been validated with empirical data. We tested this assumption using a case study of seagrass in a large, inverse estuary in South Australia (Spencer Gulf). We compared three different seagrass condition indices, based on survey data collected in the field, to scores from a spatial cumulative impact model for the study area. One condition index showed no relationship with cumulative impact, whilst the other two indices had very small, negative relationships with cumulative impact. These results suggest that one of the most commonly used methods for assessing cumulative impacts on marine systems is not robust enough to accurately reflect the effect of multiple stressors on seagrasses; possibly due to the number and generality of assumptions involved in the approach. Future methods should acknowledge the complex relationships between stressors, and the impact these relationships can have on ecosystems. This outcome highlights the need for greater evaluation of cumulative impact assessment outputs and the need for data-driven approaches. Our results are a caution for marine scientists and resource managers who may rely on spatial cumulative impact assessment outputs for informing policy and decision-making.
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Affiliation(s)
- Jackson Stockbridge
- School of Biological Sciences and Environment Institute, University of Adelaide, SA 5005, Australia.
| | - Alice R Jones
- School of Biological Sciences and Environment Institute, University of Adelaide, SA 5005, Australia; Government of South Australia Department for Environment and Water, Adelaide, South Australia 5000, Australia.
| | - Sam G Gaylard
- School of Biological Sciences and Environment Institute, University of Adelaide, SA 5005, Australia; Environment Protection Authority, 211 Victoria Square, GPO Box 2607, Adelaide, SA 5001, Australia.
| | - Matthew J Nelson
- Environment Protection Authority, 211 Victoria Square, GPO Box 2607, Adelaide, SA 5001, Australia.
| | - Bronwyn M Gillanders
- School of Biological Sciences and Environment Institute, University of Adelaide, SA 5005, Australia.
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O'Brien KR, Waycott M, Maxwell P, Kendrick GA, Udy JW, Ferguson AJP, Kilminster K, Scanes P, McKenzie LJ, McMahon K, Adams MP, Samper-Villarreal J, Collier C, Lyons M, Mumby PJ, Radke L, Christianen MJA, Dennison WC. Seagrass ecosystem trajectory depends on the relative timescales of resistance, recovery and disturbance. MARINE POLLUTION BULLETIN 2018; 134:166-176. [PMID: 28935363 DOI: 10.1016/j.marpolbul.2017.09.006] [Citation(s) in RCA: 47] [Impact Index Per Article: 6.7] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 03/31/2017] [Revised: 06/30/2017] [Accepted: 09/06/2017] [Indexed: 05/20/2023]
Abstract
Seagrass ecosystems are inherently dynamic, responding to environmental change across a range of scales. Habitat requirements of seagrass are well defined, but less is known about their ability to resist disturbance. Specific means of recovery after loss are particularly difficult to quantify. Here we assess the resistance and recovery capacity of 12 seagrass genera. We document four classic trajectories of degradation and recovery for seagrass ecosystems, illustrated with examples from around the world. Recovery can be rapid once conditions improve, but seagrass absence at landscape scales may persist for many decades, perpetuated by feedbacks and/or lack of seed or plant propagules to initiate recovery. It can be difficult to distinguish between slow recovery, recalcitrant degradation, and the need for a window of opportunity to trigger recovery. We propose a framework synthesizing how the spatial and temporal scales of both disturbance and seagrass response affect ecosystem trajectory and hence resilience.
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Affiliation(s)
- Katherine R O'Brien
- School of Chemical Engineering, The University of Queensland, St Lucia 4072, Queensland, Australia.
| | - Michelle Waycott
- School of Biological Sciences, The University of Adelaide, Adelaide, SA 5005, Australia; State Herbarium of South Australia, Botanic Gardens and State Herbarium, Department of Environment and Natural Resources, GPO Box 1047, Adelaide, SA, Australia
| | - Paul Maxwell
- School of Chemical Engineering, The University of Queensland, St Lucia 4072, Queensland, Australia; Healthy Land and Water, PO Box 13204, George St, Brisbane 4003, Queensland, Australia
| | - Gary A Kendrick
- The Oceans Institute (M470), The University of Western Australia, 35 Stirling Highway, Crawley, WA 6009, Australia; School of Biological Sciences, The University of Western Australia, 35 Stirling Highway, Crawley, WA 6009, Australia
| | - James W Udy
- Healthy Land and Water, PO Box 13204, George St, Brisbane 4003, Queensland, Australia; School of Earth, Environmental and Biological Sciences, Queensland University of Technology, P.O. Box 2434, Brisbane, Queensland 4001, Australia
| | - Angus J P Ferguson
- NSW Office of Environment and Heritage, PO Box A290, Sydney South, NSW 1232, Australia
| | - Kieryn Kilminster
- School of Biological Sciences, The University of Western Australia, 35 Stirling Highway, Crawley, WA 6009, Australia; Department of Water and Environmental Regulation, Locked Bag 33, Cloisters Square, Perth, WA 6842, Australia
| | - Peter Scanes
- NSW Office of Environment and Heritage, PO Box A290, Sydney South, NSW 1232, Australia
| | - Len J McKenzie
- Centre for Tropical Water and Aquatic Ecosystem Research (TropWATER), James Cook University, Cairns, Queensland 4870, Australia
| | - Kathryn McMahon
- School of Sciences, Edith Cowan University, WA, 6027, Australia; Centre for Marine Ecosystems Research, Edith Cowan University, WA, 6027, Australia
| | - Matthew P Adams
- School of Chemical Engineering, The University of Queensland, St Lucia 4072, Queensland, Australia
| | - Jimena Samper-Villarreal
- Marine Spatial Ecology Lab, The University of Queensland, St Lucia, Queensland 4072, Australia; Centro de Investigación en Ciencias del Mar y Limnología, Universidad de Costa Rica, San Pedro, 11501-2060, San José, Costa Rica
| | - Catherine Collier
- Centre for Tropical Water and Aquatic Ecosystem Research (TropWATER), James Cook University, Cairns, Queensland 4870, Australia
| | - Mitchell Lyons
- Centre for Ecosystem Science, School of Biological, Earth and Environmental Sciences, University of New South Wales, 2052 NSW, Australia
| | - Peter J Mumby
- Marine Spatial Ecology Lab, The University of Queensland, St Lucia, Queensland 4072, Australia
| | - Lynda Radke
- Coastal, Marine and Climate Change Group, Geoscience Australia, GPO Box 378, Canberra, ACT 2601, Australia
| | - Marjolijn J A Christianen
- Groningen Institute of Evolutionary Life Sciences (GELIFES), University of Groningen, P.O. Box 11103, 9700, CC, Groningen, Netherlands
| | - William C Dennison
- University of Maryland Center for Environmental Science, Cambridge, MD 21613, USA
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Schultz ST, Kruschel C, Bakran-Petricioli T, Petricioli D. Error, Power, and Blind Sentinels: The Statistics of Seagrass Monitoring. PLoS One 2015; 10:e0138378. [PMID: 26367863 PMCID: PMC4569085 DOI: 10.1371/journal.pone.0138378] [Citation(s) in RCA: 8] [Impact Index Per Article: 0.8] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 05/17/2015] [Accepted: 08/28/2015] [Indexed: 11/19/2022] Open
Abstract
We derive statistical properties of standard methods for monitoring of habitat cover worldwide, and criticize them in the context of mandated seagrass monitoring programs, as exemplified by Posidonia oceanica in the Mediterranean Sea. We report the novel result that cartographic methods with non-trivial classification errors are generally incapable of reliably detecting habitat cover losses less than about 30 to 50%, and the field labor required to increase their precision can be orders of magnitude higher than that required to estimate habitat loss directly in a field campaign. We derive a universal utility threshold of classification error in habitat maps that represents the minimum habitat map accuracy above which direct methods are superior. Widespread government reliance on blind-sentinel methods for monitoring seafloor can obscure the gradual and currently ongoing losses of benthic resources until the time has long passed for meaningful management intervention. We find two classes of methods with very high statistical power for detecting small habitat cover losses: 1) fixed-plot direct methods, which are over 100 times as efficient as direct random-plot methods in a variable habitat mosaic; and 2) remote methods with very low classification error such as geospatial underwater videography, which is an emerging, low-cost, non-destructive method for documenting small changes at millimeter visual resolution. General adoption of these methods and their further development will require a fundamental cultural change in conservation and management bodies towards the recognition and promotion of requirements of minimal statistical power and precision in the development of international goals for monitoring these valuable resources and the ecological services they provide.
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Affiliation(s)
- Stewart T. Schultz
- Department of Ecology, Agriculture, and Aquaculture, University of Zadar, M. Pavlinovica bb, 23000 Zadar, Croatia
- * E-mail:
| | - Claudia Kruschel
- Department of Ecology, Agriculture, and Aquaculture, University of Zadar, M. Pavlinovica bb, 23000 Zadar, Croatia
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Fitch JE, Cooper KM, Crowe TP, Hall-Spencer JM, Phillips G. Response of multi-metric indices to anthropogenic pressures in distinct marine habitats: the need for recalibration to allow wider applicability. MARINE POLLUTION BULLETIN 2014; 87:220-229. [PMID: 25127499 DOI: 10.1016/j.marpolbul.2014.07.056] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.1] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 11/26/2013] [Revised: 07/23/2014] [Accepted: 07/24/2014] [Indexed: 06/03/2023]
Abstract
Sustainable exploitation of coastal ecosystems is facilitated by tools which allow reliable assessment of their response to anthropogenic pressures. The Infaunal Quality Index (IQI) and Multivariate-AMBI (M-AMBI) were developed to classify the ecological status (ES) of benthos for the Water Framework Directive (WFD). The indices respond reliably to the impacts of organic enrichment in muddy sand habitats, but their applicability across a range of pressures and habitats is less well understood. The ability of the indices to predict changes in response to pressures in three distinct habitats, intertidal muddy sand, maerl and inshore gravel, was tested using pre-existing datasets. Both responded following the same patterns of variation as previously reported. The IQI was more conservative when responding to environmental conditions so may have greater predictive value in dynamic habitats to provide an early-warning system to managers'. Re-calibration of reference conditions is necessary to reliably reflect ES in different habitats.
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Affiliation(s)
- Jayne E Fitch
- Environment Agency, Kingfisher House, Goldhay Way, Peterborough PE2 5ZR, UK.
| | - Keith M Cooper
- The Centre for Environment, Fisheries and Aquaculture Science, Lowestoft Laboratory, Pakefield Road, Suffolk NR33 0HT, UK.
| | - Tasman P Crowe
- Earth Institute and School of Biology and Environmental Science, Science Centre West, University College Dublin, Belfield, Dublin 4, Ireland.
| | - Jason M Hall-Spencer
- Marine Biology and Ecology Research Centre, Plymouth University, Plymouth PL4 8AA, UK.
| | - Graham Phillips
- Environment Agency, Kingfisher House, Goldhay Way, Peterborough PE2 5ZR, UK.
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