Michelle C. Jackson’s research while affiliated with Imperial College London and other places

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Publications (72)


Experimental design
On the left, schematic representation of the mesocosms heated with a gradient of temperatures (from +1 to + 8 °C above ambient). Zooplankton samples were collected with a plankton net in Spring and Autumn 2019 and analysed with a FlowCam (High- throughput flow cytometry coupled with machine learning), if smaller than 1 mm, and with a microscope if bigger than 1 mm, to obtain body measurements and abundance data.
Effect of warming on community body size and biomass
a Effect of warming on average community Body size (y-axes, transformed in log10) of all measured individuals in each mesocosm (n mesocosms = 72) for each temperature (x-axes, F1,70 = 25.037, Adjusted R² = 0.253, p < 0.05). Linear model is fitted showing the confidence intervals. b Effect of warming on the average community Biomass (y-axes, transformed in log10) across the mesocosms (n mesocosms = 72) for each temperature (x-axes, F1,63.6 = 1.1290, Adjusted R² = −0.003, p = 0.2920).
PCA Biplots of Taxa Abundance and Body Size with Temperature
a The biplot displays the results of principal component analysis (PCA) conducted on the taxa abundance per mesocosm averaged over the sampling times. Each point represents an individual mesocosm, and its position in the plot reflects its projection onto the first two principal components (PC1, x-axes and PC2, y-axes). The first axis explains 22.9% of the variance, while the second 20.7%. The length and direction of the arrows represent the contribution and direction of the taxa abundance to the principal components (PC1 and PC2). b The biplot displays the results of principal component analysis (PCA) conducted on the individual body size averaged over the sampling times. Each point represents an individual mesocosm, and its position in the plot reflects its projection onto the first two principal components (PC1, x-axes and PC2, y-axes). The first axis explains 32.4% of the variance, while the second 20.1%. The length and direction of the arrows represent the contribution to the principal components (PC1 and PC2) and direction of the abundance of individuals with body size which fell in each bin (from 1 -larger individuals, to 7- smaller individuals). For both PCAs, temperature across samples is overlayed on the graphic, represented by a brown arrow. The colour scale indicates deviations of temperature from ambient levels, ranging from 0 °C (dark blue – control mesocosms) to 8 °C (dark red), for each mesocosm.
Zooplankton Body Mass vs Warming
a Relationships between warming (x-axes, in C) and average body mass (y axes, mean values in log10 scale, expressed in units of carbon (µg C)) in the different zooplankton taxa (total n of zooplankton = 18174 ind.). The best fitted model between segmented regression and linear model was chosen based on the AIC criterion. For each model, number of individuals and slope values are indicated for each taxon and when the segmented model was the best fit, a green triangle marks the position of the threshold points. b Slopes of the model for the different taxa, ranked from the steepest to the gentler slope. The shadow around the slope corresponds to the 95% confidence intervals.
Results of segmented vs linear regression analysis on the influence of the gradient of temperatures on population and community zooplankton average body size
Warming alters plankton body-size distributions in a large field experiment
  • Article
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February 2025

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135 Reads

Communications Biology

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Alex J. Dumbrell

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The threat of climate change has renewed interest in the responses of communities and ecosystems to warming, with changes in size spectra expected to signify fundamental shifts in the structure and dynamics of these multispecies systems. While substantial empirical evidence has accumulated in recent years on such changes, we still lack general insights due to a limited coverage of warming scenarios that span spatial and temporal scales of relevance to natural systems. We addressed this gap by conducting an extensive freshwater mesocosm experiment across 36 large field mesocosms exposed to intergenerational warming treatments of up to +8 °C above ambient levels. We found a nonlinear decrease in the overall mean body size of zooplankton with warming, with a 57% reduction at +8 °C. This pattern was broadly consistent over two tested seasons and major taxonomic groups. We also detected some breakpoints in the community-level size-temperature relationship, indicating that the system’s response shifts noticeably above a certain level of warming. These results underscore the need to capture intergenerational responses to large gradients in warming at appropriate scales in time and space in order to better understand the effects of warming on natural communities and ecosystems.

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Variability of functional and biodiversity responses to global change factors in experimental microbial soil systems
A The proportion of qualitative mismatches (one responds positively and the other negatively) between thirteen aggregate properties including three measures of diversity (richness, Shannon index, and Chao index), two broad ecosystem functions (biomass and respiration), and eight narrow ecosystem functions subdivided into P-cycling enzymes (phosphatase), N-cycling enzymes (N-acetyl-beta-glucosaminidase), hydrolytic C-cycling enzymes (beta-xylosidase, cellobiodydrolase, beta-glucosidase, and alpha-glucosidase), and oxidative C-cycling enzymes (peroxidase and phenol oxidase). B Correlations between the responses of three specific pairs of aggregate properties: (1) biomass and respiration, (2) biomass and richness, and (3) Chao index and phosphatase. Points that fall in the blue areas of the plots were cases when the two metrics responded in the same way to a perturbation in a given experiment, while points that fall in the red areas were cases when there were qualitative mismatches between observations. The proportion of points that are red in these figures corresponds to the proportion of mismatches reported in (A).
Geometrical approach for relating the collinearity of functions to mismatches in their observations of perturbations
A Perturbations can be viewed as displacement vectors in community state space. Here a hypothetical community of a bacterial species and a fungal species is independently impacted by two perturbations, represented by the black arrows from the initial state of the community (I) to the points A and B. B Measures of ecosystem function can be represented as positive directions in this state-space. C Perturbed states are plotted in a space where the initial state of the community is at the origin and each axis describes the response of each species to a perturbation. Here the displacement vectors associated with the independent perturbations A and B from (A) are projected onto the directions representing total biomass and plastic decomposition. For A, both functions observe negative responses. However, for B there is a mismatch in the observations of the functions: total biomass responds positively while plastic decomposition responds negatively. D For two functions, the zones of mismatches in their observations can be found by drawing lines perpendicular to the functions that go through the origin. Aggregate properties will observe different responses for perturbations that fall between these lines (i.e. in the red zones). The angle between the two functions determines the size of the zones of mismatches. The three pairs of functions include (i) a broad and a narrow function, (ii) two broad functions, and (iii) two narrow functions. E Over many in silico perturbation experiments, the proportion of mismatches between functions can be predicted by the angle between them in radians (θ) divided by the number π. Two broad functions (ii) would have high collinearity and a low proportion of mismatches, one broad and one narrow function, (i) would have moderate collinearity and a moderate proportion of mismatches, while two narrow functions, and (iii) would have low collinearity and a high proportion of mismatches (unless they were performed by the same species). The inset shows that the proportion of mismatches between a function and total biomass is a very good predictor of the broadness of that function.
Mismatches between functions in their responses to perturbations can be related to the response diversity of the underlying community
A The proportion of mismatches between functions can be predicted by the angle between them in radians (θ) divided by the number π only when perturbations are unbiased at the population level. If, however, there is population-level consistency in responses to the perturbations then there are fewer mismatches than predicted as perturbations tend to fall in the mostly positive or mostly negative areas of state space, which happen to overlap with the zones of consistent observations for linear functions. B A notion of the response diversity of a perturbation, the consistency of population-level responses, can be estimated from the relative deviation from our baseline expectation Eq. (1).
Mismatches between functions and diversity in their responses to perturbations can be related to the biomass scaling of those perturbations
A The angle between total biomass and the gradient of a diversity index (here q = 2) predicts the proportion of mismatches between them. Specifically, the relevant angle is between total biomass and the gradient of diversity after they have been scaled by the biomass of each species (θ*). When perturbations are scaled by species biomass (scaling exponent α > 0) total biomass and diversity can effectively become opposite functions. Points above the dashed red line showcase where there is a systematic mismatch in the observations of total biomass and diversity. B How much a perturbation is scaled by biomass can be estimated from the proportion of mismatches between function and diversity.
Reanalysis of the empirical data
A Results of the validation test, formally described in Supplementary Note 2, for the entire dataset (top) and for the grasslands data in orange and forest data in green (bottom). B Force-directed network constructed with the Kamada–Kawai path-length cost-function using the matrix of mismatches from the grasslands dataset as the adjacency matrix. The colour of the edges corresponds to the proportion of mismatches. The functions are microbial respiration (“RES”'), microbial biomass (“BIO”), phenol oxidase (“PO”), α-1,4-glucosidase (“AG”), β-1,4-glucosidase (“BG”), cellobiohydrolase (“CEL”), β-1,4-xylosidase (“XYL”), N-acetyl-β-glucosaminidase (“NAG”), and phosphatase (“AP”). C Estimates for the broadness based on mismatches between total biomass for five functions: microbial respiration, net N mineralization rate, phenol oxidase (“PO”), β-1,4-xylosidase (“XYL”), and phosphatase (“AP”). The size of the points corresponds to the number of observations that the proportion of mismatches is based on. D Estimates for the response diversity of perturbations based on the mismatches between total biomass and respiration (two functions with many shared observations). E Estimates for the biomass scaling of perturbations based on the mismatches between total biomass and Shannon diversity (the function and diversity metric with most shared observations). For parts (D, E) the size of the points corresponds to the number of observations and the perturbations are: elevated carbon dioxide (“eCO2”), nitrogen addition (“N”), phosphorus addition (“P”), warming (“W”), elevated precipitation (“PPT”), and the conversion of native ecosystems to secondary ecosystems (“NEtoSec”), to pasture (“NEtoPas”), to plantations (“NEtoPlant”), or to agriculture (“NEtoAgr”).
Variability of functional and biodiversity responses to perturbations is predictable and informative

November 2024

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345 Reads

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1 Citation

Perturbations such as climate change, invasive species and pollution, impact the functioning and diversity of ecosystems. However diversity has many meanings, and ecosystems provide a plethora of functions. Thus, on top of the various perturbations that global change represents, there are also many ways to measure a perturbation’s ecological impact. This leads to an overwhelming response variability, which undermines hopes of prediction. Here, we show that this variability can instead provide insights into hidden features of functions and of species responses to perturbations. By analysing a dataset of global change experiments in microbial soil systems we first show that the variability of functional and diversity responses to perturbations is not random; functions that are mechanistically similar tend to respond coherently. Furthermore, diversity metrics and broad functions (e.g. total biomass) systematically respond in opposite ways. We then formalise these observations to demonstrate, using geometrical arguments, simulations, and a theory-driven analysis of the empirical data, that the response variability of ecosystems is not only predictable, but can also be used to access useful information about species contributions to functions and population-level responses to perturbations. Our research offers a powerful framework for understanding the complexity of ecological responses to global change.


Warming reduces trophic diversity in high-latitude food webs

October 2024

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214 Reads

Global Change Biology

The physical effects of climate warming have been well documented, but the biological responses are far less well known, especially at the ecosystem level and at large (intercontinental) scales. Global warming over the next century is generally predicted to reduce food web complexity, but this is rarely tested empirically due to the dearth of studies isolating the effects of temperature on complex natural food webs. To overcome this obstacle, we used ‘natural experiments’ across 14 streams in Iceland and Russia, with natural warming of up to 20°C above the coldest stream in each high‐latitude region, where anthropogenic warming is predicted to be especially rapid. Using biomass‐weighted stable isotope data, we found that community isotopic divergence (a universal, taxon‐free measure of trophic diversity) was consistently lower in warmer streams. We also found a clear shift towards greater assimilation of autochthonous carbon, which was driven by increasing dominance of herbivores but without a concomitant increase in algal stocks. Overall, our results support the prediction that higher temperatures will simplify high‐latitude freshwater ecosystems and provide the first mechanistic glimpses of how warming alters energy transfer through food webs at intercontinental scales.


Filling in evidence gaps for the safe deployment of offshore Geological Carbon Storage

September 2024

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85 Reads

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1 Citation

This report is the final output of an Agile Initiative Sprint, addressing the question, “What do we need to know to safely store CO2 beneath our shelf seas?” The writers aim to improve understanding of the environmental risks and opportunities associated with CO2 storage in offshore reservoirs, to deliver new research, and to integrate existing knowledge from across research and policy areas, identifying gaps and areas requiring further research. This Sprint concluded in June 2024.



Calanus glacialis copepods were subject to an array of different stressors, alone or in combinations: warming (W), microplastics (MP) and pyrene (PYR) in a full factorial design, with three temporal regimes (1): Pulse (2 Pulses & 2 Recovery), Press (continuous exposure with a recovery at the end of the stress application). A control treatment (Ctrl) was set and kept without stressor exposure. The experiment lasted 14 days.
Effects of individual and all the stressor combinations on C. glacialis average survival (mean survival, y‐axes) starting with 9 copepods per bottle at Day 0. Stressor phases are denoted in yellow, whilst recovery phases are in blue. Panel (a) illustrates the pulse‐temporal stress scenario, whilst panel (b) shows the press‐temporal stress scenario. The length for each phase is reported in brackets, in days (dd). Asterisks (*) indicate the statistical differences between the control and the treatments based on the number of survivals (Table S1).
Decrease in C. glacialis mean survival in the press‐temporal scenario. Panel (a) shows the cumulative percentage of total survival in the three subsequential exposures. Panel (b) represents the mean copepod survival (mean ± SE) for all the combinations of multiple stressors over the three subsequential stressor exposures. Shapes indicate the different treatments at each sampling point and the grey areas are the 95% confident intervals for each treatment.
Temporal patterns in multiple stressors shape the vulnerability of overwintering Arctic zooplankton

June 2024

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94 Reads

The Arctic polar nights bring extreme environmental conditions characterised by cold and darkness, which challenge the survival of organisms in the Arctic. Additionally, multiple anthropogenic stressors can amplify the pressure on the fragile Arctic ecosystems during this period. Determining how multiple anthropogenic stressors may affect the survival of Arctic life is crucial for ecological risk assessments and management, but this topic is understudied. For the first time, our study investigates the complex interactions of multiple stressors, exploring stressor temporal dynamics and exposure duration on a key Arctic copepod Calanus glacialis during the polar nights. We conducted experiments with pulse (intermittent) and press (continuous) exposure scenarios, involving microplastics, pyrene and warming in a fully factorial design. We observed significant effects on copepod survival, with pronounced impacts during later stressor phases. We also detected two‐way interactions between microplastics and pyrene, as well as pyrene and warming, further intensified with the presence of a third stressor. Continuous stressor exposure for 9 days (press‐temporal scenario) led to greater reductions in copepod survival compared to the pulse‐temporal scenario, characterised by two 3‐day stressor exposure phases. Notably, the inclusion of recovery phases, free from stressor exposure, positively influenced copepod survival, highlighting the importance of temporal exposure dynamics. We did not find behaviour to be affected by the different treatments. Our findings underscore the intricate interactions amongst multiple stressors and their temporal patterns in shaping the vulnerability of overwintering Arctic copepods with crucial implications for managing Arctic aquatic ecosystems under the fastest rate of ongoing climate change on earth.


Studying interactions among anthropogenic stressors in freshwater ecosystems: A systematic review of 2396 multiple‐stressor experiments

June 2024

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837 Reads

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12 Citations

Ecology Letters

Understanding the interactions among anthropogenic stressors is critical for effective conservation and management of ecosystems. Freshwater scientists have invested considerable resources in conducting factorial experiments to disentangle stressor interactions by testing their individual and combined effects. However, the diversity of stressors and systems studied has hindered previous syntheses of this body of research. To overcome this challenge, we used a novel machine learning framework to identify relevant studies from over 235,000 publications. Our synthesis resulted in a new dataset of 2396 multiple‐stressor experiments in freshwater systems. By summarizing the methods used in these studies, quantifying trends in the popularity of the investigated stressors, and performing co‐occurrence analysis, we produce the most comprehensive overview of this diverse field of research to date. We provide both a taxonomy grouping the 909 investigated stressors into 31 classes and an open‐source and interactive version of the dataset (https://jamesaorr.shinyapps.io/freshwater‐multiple‐stressors/). Inspired by our results, we provide a framework to help clarify whether statistical interactions detected by factorial experiments align with stressor interactions of interest, and we outline general guidelines for the design of multiple‐stressor experiments relevant to any system. We conclude by highlighting the research directions required to better understand freshwater ecosystems facing multiple stressors.


Study region map and Whittaker biome plot, and the effects of stream temperature and biogeography variables on species richness
a Location of the five regions and b the biome area each region occupies, including how this could be reshaped with climate projections. Temperature and precipitation are given as an annual average and total, respectively. This figure was made using the plotbiomes package in R (https://valentinitnelav.github.io/plotbiomes/). c General linear model’s showed that diatom richness was predicted by a combination of temperature, d biome area (in millions of km²), e and NDVI. f For invertebrates, richness was predicted by temperature, and g NDVI. Symbols in c–g represent a single stream, coloured lines are the linear model for each region, and the dashed black line represents the overall linear trend with 90% confidence intervals.
Effects of stream temperature on invertebrate biomass
Our general linear model’s showed that biomass consistently increased with temperature in all five regions regardless of biogeography. Symbols represent a single stream, coloured lines are the linear model for each region, and the dashed black line represents the overall linear trend with 90% confidence intervals.
Effects of study region and stream temperature on community composition (relative abundance)
Detrended correspondence analysis plots are shown for all diatom (a, b) and invertebrate (c, d) species, where each point represents the community in a single stream. Symbols represent the five regions and colours scale from ambient cold (blue) to warm (red) streams. Plots either show passively overlaid environmental variables (a, c), or important species which vary between the communities (b, d). Full results are in Supplementary Table 5.
Regional impacts of warming on biodiversity and biomass in high latitude stream ecosystems across the Northern Hemisphere

March 2024

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511 Reads

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4 Citations

Communications Biology

Warming can have profound impacts on ecological communities. However, explorations of how differences in biogeography and productivity might reshape the effect of warming have been limited to theoretical or proxy-based approaches: for instance, studies of latitudinal temperature gradients are often conflated with other drivers (e.g., species richness). Here, we overcome these limitations by using local geothermal temperature gradients across multiple high-latitude stream ecosystems. Each suite of streams (6-11 warmed by 1-15°C above ambient) is set within one of five regions (37 streams total); because the heating comes from the bedrock and is not confounded by changes in chemistry, we can isolate the effect of temperature. We found a negative overall relationship between diatom and invertebrate species richness and temperature, but the strength of the relationship varied regionally, declining more strongly in regions with low terrestrial productivity. Total invertebrate biomass increased with temperature in all regions. The latter pattern combined with the former suggests that the increased biomass of tolerant species might compensate for the loss of sensitive species. Our results show that the impact of warming can be dependent on regional conditions, demonstrating that local variation should be included in future climate projections rather than simply assuming universal relationships.


Pet treatments could be harming freshwater life. FBA Info Note No2 https://www.fba.org.uk/info-notes/pet-treatments-could-be-harming-freshwater-life

February 2024

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42 Reads

The use of flea treatment on pets could be causing problems in English rivers and lakes. The chemicals used in the treatments are toxic to freshwater invertebrates and have been detected in rivers across England despite severe restrictions on agricultural use since 2018. Reducing the risk posed by these chemicals requires improved scientific knowledge, better monitoring and stricter regulatory management. Vets and pet owners may have a very important part to play because they can help by simple changes in behaviour. https://www.fba.org.uk/info-notes/pet-treatments-could-be-harming-freshwater-life


Modelling the potential for local management practices to offset climate change impacts on freshwater macroinvertebrate communities

January 2024

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188 Reads

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1 Citation

Freshwater Biology

A robust understanding of the interactions between global and local anthropogenic stressors is crucial for ecosystem management in the Anthropocene. Manipulative experiments in the laboratory or in the field can be used to build knowledge about the physiological and ecological effects of stressors, but predicting the combined landscape‐scale effects of global stressors such as climate change, and local stressors such as land‐use change requires a different approach. Here we used water quality and hydrology process‐based models of entire river catchments in combination with a large biomonitoring dataset to predict the responses of macroinvertebrate communities under different climate change and land‐use change scenarios. Using the River Thames in the U.K. as a model system, we predicted changes in water quality (temperature, flow, phosphorus [P], nitrogen, dissolved oxygen [DO]) and subsequent changes in macroinvertebrate communities for two climate change scenarios, individually and in combination with intensified agriculture and reduced P pollution (representing improved wastewater treatment). Our models predicted that water‐quality changes associated with climate change may not influence total species richness, but that community composition will shift towards more pollution‐tolerant and common taxa based on responses of community indices and taxon‐specific responses. We also found that the negative impacts of climate change on water quality (e.g., increased P concentration, decreased DO concentration) accumulate through the catchment, but that local land‐use practices influencing P dynamics can modify this trend. Furthermore, although the intensified agriculture scenario was predicted to have minimal impacts on macroinvertebrate communities (a result potentially related to shifting baselines as the Thames is already heavily polluted), we found that reduced P pollution resulting from improved wastewater treatment was able to mostly offset the negative impacts of climate change on macroinvertebrate communities. Our results demonstrate that using process‐based models to study networks of interacting stressors at a landscape scale can provide useful insights into the ecological impacts of anthropogenic global change, and adds support to the idea that management of local stressors has the potential to mitigate some of the impacts of climate change on ecosystems.


Citations (53)


... Noteworthily, components of the ZSG were repeatedly remobilised throughout the Mesozoic and Cenozoic to form complex salt structures (van Hoorn, 1987;Stewart and Coward, 1995;Geluk, 1999;Underhill, 2003;Peryt et al., 2010;Pharaoh et al., 2010;Grant et al., 2019), which controlled later structural (halokinetic) styles and depositional patterns across a vast portion of the SPB (van Hoorn, 1987;Stewart and Coward, 1995;Stewart, 1996;Stewart, 2007). For these specific reasons, the ZSG of the Southern North Sea has attracted particular scientific attention for carbon storage purposes (Underhill et al., 2009;Brackenridge et al., 2023;Sutton et al., 2024). ...

Reference:

Major heterogeneity in evaporitic depositional systems: The genesis of kilometre-scale gypsum networks in the Zechstein Basin
Filling in evidence gaps for the safe deployment of offshore Geological Carbon Storage

... Combined effects of plastic pollution and other stressors, like climate change, can also exacerbate the detrimental effects creating a complex web of challenges: plastics not only pose direct threats to habitats and wildlife but could also interact synergistically with climate-related stressors, potentially magnifying their ecological impacts (Chowdhury et al., 2022;Sharma et al., 2023). This linkage has been until now only hypothesized for marine environments (Ford et al., 2022), remaining almost neglected for fresh waters (but see Parker et al., 2024). The increased temperature and the prolonged period of drought exacerbate the effects of MP pollution on freshwater organisms, leading to higher exposure concentrations and more frequent anoxia events (Cabral et al., 2019). ...

Microplastic-stressor responses are rarely synergistic in freshwater fishes: A meta-analysis

The Science of The Total Environment

... In recent years, there has been an increase in attention surrounding the use of performance curves (also referred to as response norms, reaction norms, dose-response curves, stressor-response functions) to understand multiple stressor interactions (Boyd et al. 2018;Collins, Whittaker, and Thomas 2022;Harley et al. 2017;Kreyling, Jentsch, and Beier 2014;Kreyling et al. 2018;van Moorsel et al. 2023;Orr et al. 2024;Pirotta et al. 2022;Rosenfeld et al. 2022;Schäfer et al. 2023;Segurado et al. 2022). This approach measures biological responses (e.g., population growth or mortality) to gradients of environmental parameters (Boyd et al. 2018). ...

Studying interactions among anthropogenic stressors in freshwater ecosystems: A systematic review of 2396 multiple‐stressor experiments

Ecology Letters

... For instance, Hogg and Williams (1996) found a reduction in the density of taxa at warmer temperatures and, for many species, a reduction in body size at maturity when artificially increasing steam temperatures. However, Jackson et al. (2024) found that total biomass increased with temperature over a natural thermal gradient of streams, with losses in sensitive taxa potentially compensated by more tolerant taxa. ...

Regional impacts of warming on biodiversity and biomass in high latitude stream ecosystems across the Northern Hemisphere

Communications Biology

... Process-based simulation models can simulate realistic spatiotemporal stressor profiles and, thereby, significantly contribute to a better mechanistic understanding of joint effects and related interactions across scales [6,24,25]. In addition, they support the development of corresponding theory [11,26]. ...

Modelling the potential for local management practices to offset climate change impacts on freshwater macroinvertebrate communities

Freshwater Biology

... Furthermore, seasonality might play a role in the responses of zooplankton to warming. In fact, low food (i.e., phytoplankton) availability and high predator pressure in the winter and autumn season might lead to zooplankton reduced body size 57,58 . Taxonomic identity can also affect the body size responses to temperature of different zooplankton, which might be due to different food adaptability and competitive ability of different taxon groups 49 . ...

Winter is coming: Interactions of multiple stressors in winter and implications for the natural world
  • Citing Article
  • September 2023

Global Change Biology

... The water industry continues to take advantage of RNAGs' flaws to play down the impacts of untreated wastewater discharges (T3 and T5; Box 4). Albini et al. 70 , in a modelling study of four different rivers, recently concluded that sewage discharge significantly impacts water quality and benthic riverine communities, regardless of the surrounding land uses. Deflecting blame without comprehensive monitoring has delayed regulation and policy change (T19). ...

The combined effects of treated sewage discharge and land use on rivers

Global Change Biology

... These are most likely appear where untreated or inadequately treated wastewater is discharged into the river (Curtis and Harrington 1971). "Sewage fungus" proliferates in saprobic rivers, and their presence is often a sign of severe pollution (Albini et al. 2023). In our case, the high abundance of Sphaerotilus in the biofilm samples (60% relative abundance) clearly indicated that the Danube might have been affected by some kind of faecal pollution. ...

Early detection and environmental drivers of sewage fungus outbreaks in rivers

... The interaction of multiple stressors has exacerbated the existing vulnerabilities within the aquaculture industry (Freduah et al. 2017;Deb and Haque 2017;Sánchez-Jerez et al. 2022). Although previous studies have explored the impacts of multiple stressors on traditional aquaculture systems, research specifically focusing on seaweed farming remains limited (Matoju et al. 2022;Wear et al. 2023). Additionally, there is a scarcity of empirical evidence regarding the effects of these stressors at the household and family levels, as well as on the differential vulnerabilities between fishing households (Bunce et al. 2010;Bennett et al. 2015;Onyenekwe et al. 2022), and there is still a lack of literature addressing the vulnerability of aquaculture to multiple stressors (Sarà et al. 2018). ...

What does the future look like for kelp when facing multiple stressors?

... In recent years, there has been an increase in attention surrounding the use of performance curves (also referred to as response norms, reaction norms, dose-response curves, stressor-response functions) to understand multiple stressor interactions (Boyd et al. 2018;Collins, Whittaker, and Thomas 2022;Harley et al. 2017;Kreyling, Jentsch, and Beier 2014;Kreyling et al. 2018;van Moorsel et al. 2023;Orr et al. 2024;Pirotta et al. 2022;Rosenfeld et al. 2022;Schäfer et al. 2023;Segurado et al. 2022). This approach measures biological responses (e.g., population growth or mortality) to gradients of environmental parameters (Boyd et al. 2018). ...

Chemical Mixtures and Multiple Stressors: Same but Different?

Environmental Toxicology and Chemistry