Catherine E. Lovelock’s research while affiliated with The University of Queensland and other places

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Publications (129)


Safeguarding climate-resilient mangroves requires a small increase in the global protected area
  • Preprint
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December 2024

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110 Reads

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Climate change and anthropogenic activities threaten biodiversity and ecosystem services. Climate-smart conservation plans address these challenges by focusing protection in climate-resilient areas. However, integrating climate change in the design of conservation plans is often deemed too expensive, as it may require larger networks or protecting more costly sites. Using mangroves as a case study, we evaluated the efficiency of protecting mangroves in climate-smart versus climate-naïve reserve networks. We found that climate-smart conservation plans could provide sizable benefits for relatively small increases in protected area. Moreover, transboundary plans, involving cooperation among countries, require less area and protect more climate-resilient mangroves than nation-by-nation plans. Implementing these strategies would improve the current network of protected areas for mangroves, which currently has poor climate resilience. These findings could also be applied in other ecosystems.

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Figure 1. Open coast mangrove settings and drainage basins of the Gulf of Carpentaria.
Figure 2. Hovmőller diagram for transect 117 in Limmen Bight, western Gulf of Carpentaria. a) NDVI along the transect, rate of change of NDVI (green line) and variation in trend (indicated by r-squared, red line); b) mNDWI, rate of change in mNDWI (blue line) and variation in trend (red line); c) Google Earth images showing mangrove extent at selected years for which imagery is available.
Figure 3. Hovmőller diagrams, and graphs of NDVI change (green line) and variation in trend (red line) for transects from Blue Mud Bay in the west of the Gulf of Carpentaria in which the landward margin remains stable, but the seaward margin is either a) prograding (Transect 22) or b) retreating (Transect 46). Google Earth images indicating c) prograding mangrove fringe at the Leichhardt River and Mornington sections of the coast; d) mangrove sheltered behind spits; and e) examples of mangrove groynes (Transect 117 and Transect 215).
Figure 4. Hovmőller diagrams, graphs of NDVI change (green line) and variation in trend (red line) for a) transect 188 where chenier ridge is reworking landward through mangroves; and b) transect 228 where interior decline in NDVI in the 1990s and 2015-2016 have been associated with dieback. Aerial photographs of the complexity of dieback and recovery associated with the 2015-2016 dieback event, including c) Limmen Bight dieback and recovery, d) seaward margin dieback with variable recovery, e) mangrove fringe retreat associated with deposition of a sandy chenier ridge (near transect 188), f) interior forest dieback, g) dieback with persisting seaward mangrove, and h) extensive mangrove dieback following reworking chenier ridge. Source: TERN, Courtesy of NC Duke.
Prevalence of Mangrove Progradation in the Gulf of Carpentaria Revealed by Satellite Time Series

July 2024

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112 Reads

Journal of Coastal Research

Prevalence of mangrove progradation in the Gulf of Carpentaria revealed by satellite time series. The distribution of mangroves has been declining, predominantly driven by anthropogenic impacts, and increasingly climate change is proposed to be impacting their extent and condition. Projections of sea-level rise imply that the seaward extent of mangroves may retract with extension on the landward margin. The archive of Landsat imagery enables broad-scale regional assessment of changes through Digital Earth Australia, from 1988 to the present. Changes to the extent and condition of open coast mangroves can be interpreted using indices of vegetation and surface water conditions calculated from Landsat data. These dense timeseries data can be extracted and visualised along transects. In the Gulf of Carpentaria in northern Australia, where there are limited anthropogenic influences, we investigated shore-normal transects that were systematically spaced along a coastline of approximately 1500 km. This coastline includes a range of geomorphologically complex features such as chenier ridges, tidal creeks, spits and tide-dominated beaches. We found widespread occurrence of progradation of the seaward margin. Changes to the landward mangrove extent were highly variable. Despite the extensive dieback of mangroves in recent years, including events in the early 1990s and 2015-2016, recovery of vegetation cover was evident in subsequent years. This analytical approach offers potential to explore changes to both seaward and landward mangrove margins in open-coast settings. In contrast to highly populated coastlines where infrastructure and assets cause coastal squeeze, landward expansion of mangroves in northern Australia is anticipated across the widespread low-lying coastal plains, which offer accommodation space under a higher sea level. Observations of progradation of the mangrove seaward margin over the past three decades are contrary to expectations under sea-level rise.


Forest zone and root compartments outweigh long-term nutrient enrichment in structuring arid mangrove root microbiomes

July 2024

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41 Reads

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2 Citations

Frontiers in Forests and Global Change

Mangroves offer many important ecosystem services including carbon sequestration, serving as nursery grounds to many organisms, and acting as barriers where land and sea converge. Mangroves exhibit environmental flexibility and resilience and frequently occur in nutrient-limited systems. Despite existing research on mangrove microbiomes, the effects of nutrient additions on microbial community structure, composition, and function in intertidal and landward zones of mangrove ecosystems remain unclear. We utilized a long-term nutrient amendment study in Exmouth Gulf, Western Australia conducted in two zones, the intertidal fringe and supralittoral scrub forests, dominated by Avicennia marina . Root samples were fractionated into rhizosphere, rhizoplane and endosphere compartments and analyzed by 16S rRNA gene amplicon sequencing to determine the effects of nutrient stress on community structure and function. Our data showed species richness and evenness were significantly higher in the scrub forest zone. PERMANOVA analysis revealed a significant effect of nutrient enrichment on beta diversity ( p = 0.022, R ² = 0.012) in the fringe forest zone only. Cylindrospermopsis , which has been associated with harmful algal blooms, was found to be significantly enriched in fringe phosphate-fertilized plots and nitrogen-fixing Hyphomicrobiales were significantly depleted in the scrub nitrogen-fertilized plots. Meanwhile, root compartments and forest zone had a greater effect on beta diversity ( p = 0.001, R ² = 0.186; p = 0.001, R ² = 0.055, respectively) than nutrient enrichment, with a significant interaction between forest zone and root compartment ( p = 0.001, R ² = 0.025). This interaction was further observed in the distinct divergence identified in degradative processes of the rhizosphere compartment between the two forest zones. Degradation of aromatic compounds were significantly enriched in the fringe rhizosphere, in contrast to the scrub rhizosphere, where degradation of carbohydrates was most significant. Despite the highly significant effect of forest zone and root compartments, the long-term effect of nutrient enrichment impacted community structure and function, and potentially compromised overall mangrove health and ecosystem stability.




Fig. 1 | Total soil organic carbon stocks (SOC, Teragrams) in the top 1 m of tidal marshes. a) aggregated per 2° cell, and b) for the ten countries with the highest total SOC stock. Values refer to predicted SOC stocks after removing pixels outside the area of applicability (AOA), i.e. where we enabled the model to learn about the relationship between SOC stocks and the environmental drivers. Whiskers represent expected model error.
Fig. 2 | Global distribution of tidal marsh soil organic carbon (SOC) for a) the 0-30 cm soil layer and b) the 30-100 cm soil layer (aggregated per 2° cell). Values refer to predicted SOC per unit area (Mg C ha -1 ) after removing pixels outside the area of applicability (AOA), i.e. where we enabled the model to learn about the relationship between SOC and the environmental drivers. Cells with 0 % of pixels within the AOA are not displayed. Because fewer training data points were available in the deeper soil layer, more pixels are outside the AOA and thus fewer cells are displayed in the lower panel. Initial predicted values and the proportion of pixels in each cell within the AOA are presented in Fig. S1 and Fig. S2.
Fig. 3 | Realm level summary statistics of soil organic carbon (SOC) in a) the 0-30 cm soil layer and b) the 30-100 cm soil layer. For each soil layer (0-30 cm and 30-100 cm), the x-axis shows the proportion of the realm within the area of applicability (AOA), i.e. where we enabled the model to learn about the relationship between SOC and the environmental drivers, and the y-axis shows the average final predicted SOC, after masking out areas outside the AOA. Whiskers represent the expected model error for each prediction. Colours are mapped to realms, which correspond to the biogeographical realms of the Marine Ecoregions of the World 33 , and the global average.
Fig. 5 | Bivariate plot showing predicted SOC stocks per unit area and expected error. Values are for the initial model predictions and expected model error (i.e., not masked by the area of applicability), aggregated per 2° cell. The plot shows locations with low predictions and low error (grey), high prediction and low error (blue), low predictions and high error (yellow), and high predictions with high error (green).
Soil carbon in the world's tidal marshes

April 2024

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623 Reads

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3 Citations

Tidal marshes are threatened coastal ecosystems known for their capacity to store large amounts of carbon in their water-logged soils. Accurate quantification and mapping of global tidal marshes soil organic carbon (SOC) stocks is of considerable value to conservation efforts. Here, we used training data from 3,710 unique locations, landscape-level environmental drivers and a newly developed global tidal marsh extent map to produce the first global, spatially-explicit map of SOC storage in tidal marshes at 30 m resolution. We estimate the total global SOC stock to 1 m to be 1.44 Pg C, with a third of this value stored in the United States of America. On average, SOC in tidal marshes' 0-30 and 30-100 cm soil layers are estimated at 83.1 Mg C ha ⁻¹ (average predicted error 44.8 Mg C ha ⁻¹ ) and 185.3 Mg C ha ⁻¹ (average predicted error 105.7 Mg C ha ⁻¹ ), respectively. Our spatially-explicit model is able to capture 59% of the variability in SOC density, with elevation being the strongest driver aside from soil depth. Our study reveals regions with high prediction uncertainty and therefore highlights the need for more targeted sampling to fully capture SOC spatial variability.


The Global Biodiversity Framework’s ecosystem restoration target requires more clarity and careful legal interpretation

March 2024

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159 Reads

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10 Citations

Nature Ecology & Evolution

With the passage of the one-year anniversary of the Kunming-Montreal Global Biodiversity Framework (GBF), substantial effort is still needed to progress Target 2 — the ‘restoration target’. The restoration target guides parties to “ensure that by 2030 at least 30 per cent of areas of degraded terrestrial, inland water, and marine and coastal ecosystems are under effective restoration, in order to enhance biodiversity and ecosystem functions and services, ecological integrity and connectivity”. This target is a critical step towards upscaling global restoration, but almost every word of it provides scope for legal and ecological interpretation. This could result in markedly different on-the-ground outcomes for conservation once applied at a national level. Although nebulous targets are a common by-product of the international negotiation process, definitional uncertainty in the meaning of key terms can lead to markedly different models of implementation across different countries and make success difficult to assess and measure2,3. More fundamentally, it is crucial that the key elements of Target 2 are interpreted in the spirit of the GBF — that is, to achieve rapid, ambitious and large-scale restoration of global ecosystems, which is a critical goal given the ongoing deterioration of ecosystems globally. Here, we unpack the elements of Target 2 — none of which are defined in the GBF itself — to highlight areas of definitional ambiguity, better guide consistency in implementation and encourage genuine progress towards its achievement.


All tidal wetlands are blue carbon ecosystems

March 2024

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425 Reads

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23 Citations

BioScience

Managing coastal wetlands is one of the most promising activities to reduce atmospheric greenhouse gases, and it also contributes to meeting the United Nations Sustainable Development Goals. One of the options is through blue carbon projects, in which mangroves, saltmarshes, and seagrass are managed to increase carbon sequestration and reduce greenhouse gas emissions. However, other tidal wetlands align with the characteristics of blue carbon. These wetlands are called tidal freshwater wetlands in the United States, supratidal wetlands in Australia, transitional forests in Southeast Asia, and estuarine forests in South Africa. They have similar or larger potential for atmospheric carbon sequestration and emission reductions than the currently considered blue carbon ecosystems and have been highly exploited. In the present article, we suggest that all wetlands directly or indirectly influenced by tides should be considered blue carbon. Their protection and restoration through carbon offsets could reduce emissions while providing multiple cobenefits, including biodiversity.


Fig. 3. Hindcast accuracy. Hindcasts were evaluated against historical observations of net 171 change in mangrove extent derived from satellite remote sensing over 24 years and were 172 made using optimal pressure definition and ambiguity thresholds (i.e., 'Strict' and '75%, 173 respectively; Fig S2). Hindcast accuracy was quantified via 5-fold cross-validation as: A) 174 overall accuracy of gain/stability and loss, B) gain/stability user and producer accuracy, and 175 C) loss user and producer accuracy. Accuracy point estimates are median values and error 176 bars represent 95% confidence intervals, derived from resampled distributions of each 177 accuracy metric. Maps display D) seaward and E) landward hindcast validation and 178 discrepancies with historical observations. Red 'No Hindcast' dots represent mangrove forest 179
Fig. 4. Probabilistic forecasts of the direction of change in mangrove extent globally. 202 Baseline and scenario-based forecasts of seaward (A, B) and landward (C, D) net change 203
Network model node definitions. Nodes are variables in the model (Fig. 1). 106
Uncertainties in forecasts of ecosystem persistence under climate change

February 2024

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256 Reads

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1 Citation

Global forecasts of ecosystem responses to increasing climatic and anthropogenic pressures are needed to inform adaptation planning. However, data of appropriate spatio-temporal resolution are not typically available to parameterise complex processes at the global scale. Forecast uncertainty associated with ‘data-process’ scale incongruities must be quantified and effectively communicated to avoid over-confident decision-making. Here, we used network models to make probabilistic forecasts of the direction of change in mangrove extent globally under the SSP5-8.5 climate emissions scenario by 2040-2060. We forecast that seaward net loss is the most likely outcome in 77% [±37-78%; 95% confidence] of mangrove forest units, while 30% [±15-59%] will experience landward net gain or stability. Parameter uncertainty limited our capacity to make reliable forecasts everywhere, highlighting where current understanding and global datasets are deficient. However, with action to manage or restore, the number of mangrove forest units likely to experience net gain or stability could nearly double.


Citations (81)


... Tidal flats of estuarine mangrove wetlands have vital ecological functions for nutrient and sediment exchange (Shih and Cheng 2022). Although incomparable with mangrove-covered areas, tidal flats also possess rich nutrients and organic carbon (Nayak et al. 2018;Xie et al. 2023;Qin et al. 2024). Our study revealed significantly higher SOC, TN, and TP contents in the estuarine mangrove tidal flats than those in the non-estuarine mangrove tidal flats (Fig. 2a-c), which might be due to the effects of organic carbon inputs through river flows (Völkel et al. 2018). ...

Reference:

Soil organic carbon contents and their major influencing factors in mangrove tidal flats: a comparison between estuarine and non-estuarine areas
Fate of soil organic carbon in estuarine mangroves: Evidences from stable isotopes and lignin biomarkers
  • Citing Article
  • September 2024

CATENA

... However, these measurement depths may be insufficient and potentially introduce significant uncertainty to current estimates of carbon storage and additions to substrate volume for maintaining surface elevation. Emphasis on understanding root additions within ecosystem types, including mangrove forests (Poungparn et al. 2016;Hsiao et al. 2024) and saltmarshes (Kirwan and Guntenspergen 2015;Stagg et al. 2017) has resulted in few studies investigating root zone dynamics across complex vegetation zones or across inundation gradients that establishes the conditions for complex zonation. Further, coastal wetland root systems exhibit greater volumetric contribution to substrates relative to mass contributions per root due to pore space within root structures in mangrove aerenchyma (Lovelock et al. 2015) and saltmarsh (Ampuero Reyes and Chmura 2022). ...

Forest zone and root compartments outweigh long-term nutrient enrichment in structuring arid mangrove root microbiomes

Frontiers in Forests and Global Change

... Future studies could incorporate additional processes and gradually increase complexity. Aerial roots were omitted in this study, but they can play a key role in stability; for example, Hill et al. [37] found that detaching aerial roots from the soil halved the force required to tilt a Rhizophora stylosa tree. Mangrove canopies are often offset from the trunk due to competition and wind stress [38], which also alters the overturning moment-a factor that could be investigated in future experiments. ...

Mangrove tree strength estimated with field experiments

Ecological Engineering

... Eminently, estuaries are often environments that receive substances contaminated with pollutants, untreated urban or industrial wastewater effluents, and leaching waters from the watershed feeding the estuary (Dey & Majumdar, 2024). Another type of degradation affecting the physico-chemical quality of the estuarine ecosystem lies in poorly studied developments or sand dredging operations in the estuary (Cadier et al., 2024;Oliveira et al., 2024). Furthermore, among the repercussions of human actions on estuaries is the gradual degradation of ecological balance, usually initiated by an alteration of the physico-chemical parameters of estuarine water, leading to subsequent modification of the biological component of the hydrological system Thus, diatoms are an important part of river ecosystems (Ferhi, 2023; Sànchez-Mateo et al., 2023). ...

A standard condition and threat indicator framework for benthic marine and estuarine condition assessment

Ecological Indicators

... Recent studies have highlighted significant spatial variability in wetland carbon stocks, not only between geographically distinct coastal areas (Maxwell et al., 2024) but also within individual wetland ecosystems (Martinetto et al., 2023;Mazarrasa et al., 2023;, Puppin, Tognin, Paccagnella, et al., 2024Russell et al., 2024). These observations underscore the need to refine blue carbon assessments at spatial scales finer than the total wetland footprint, where ecomorphodynamic processes are steered • Despite covering a small fraction of wetland area, abandoned channels contribute significantly to wetland carbon dynamics • Accounting for abandoned tidal channels is needed to improve current estimates of blue carbon stocks and fluxes in coastal wetlands ...

Soil carbon in the world's tidal marshes

... The framing of the concept of 30 × 30 in our survey was necessarily simple and the ultimate wording of the 30 × 30 target (Target 3 of the Global Biodiversity Framework) contained greater detail on what needs to be protected (e.g., [32]) and how it needs to be protected. This adds to the potential complexity of achieving the target and ambiguities in interpretation, similar to some other targets in the GBF (e.g., [33]). ...

The Global Biodiversity Framework’s ecosystem restoration target requires more clarity and careful legal interpretation
  • Citing Article
  • March 2024

Nature Ecology & Evolution

... Wetlands are significant soil organic carbon sinks and sources (Nahlik & Fennessy, 2016;Tangen & Bansal, 2020). In both inland and tidally influenced wetlands, above-and below-ground productivity is frequently coupled with anoxic conditions, limiting autochthonous and allochthonous organic matter decomposition and increasing soil organic carbon stores and sink functions (Adame et al., 2024;Brinson et al., 1981;Khvorostyanov et al., 2008). As a result, wetlands are estimated to contain approximately 20%-30% of the global soil carbon (Mitsch & Gosselink, 2007). ...

All tidal wetlands are blue carbon ecosystems

BioScience

... where it is not impeded by natural or anthropogenic structures 11 . Here, we prioritise areas with higher climate resilience identi ed using an ecological network model 17 . We quanti ed climate resilience on a scale from 0 (least resilient) to 100 (most resilient), with the least and most resilient corresponding to the highest and lowest probability of loss respectively, from the model. ...

Uncertainties in forecasts of ecosystem persistence under climate change

... Changes in N cycling in flooded soils are related to decreases in oxygen concentrations, the accumulation of ammonium, and the volatilization of ammonia. Studies have shown that the primary form of dissolved inorganic N in sediment porewaters is ammonium [91]. In central Chile, it has been shown that surplus N in maize-cropping systems could be leached by the excessive irrigation water during the growing season, while up to 6% of the total nitrate load could be lost through leaching in autumn-winter during flush-flooding events [92]. ...

Nitrogen loading resulting from major floods and sediment resuspension to a large coastal embayment

The Science of The Total Environment

... Moving forward, there is a need for these large and complex communities to integrate and co-develop a shared strategy for managing the built and natural marine environment (Saunders et al. 2024). Such efforts should be conducted in conjunction with the priorities of local stakeholders to ensure buy-in and equitable and just outcomes (Morris et al. 2022;www. darpa. ...

Current extent and future opportunities for living shorelines in Australia

The Science of The Total Environment