Exploration of climate-induced shifts in historical and future distributions of marine species on the U.S. Northeast Shelf

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Non-Technical Synopsis Exploration of climate-induced shifts in historical and future distributions of marine species on the U.S. Northeast Shelf Executive Summary Kristin Kleisner Michael Fogarty Sally McGee Analie Barnett Paula Fratantoni Jennifer Greene Jonathan Hare Sean Lucey Chris McGuire Skye Morét Jay Odell Vincent Saba Laurel Smith Katherine Weaver Malin Pinsky* * demersal dwelling at or near the bottom of a body of water. assemblage a group of organisms belonging to a number of different species that co-occur in the same area and interact through trophic and spatial relationships and often share a preference for particular oceanographic characteristics. The overarching goal of this project is to advance ecosystem based management and ocean use planning in the Northeast and Mid-Atlantic regions through the analysis of historical and future distribution shifts of demersal marine species. As opposed to studies that examine shifts in distribution of individual species, this project takes an ecosystem approach and measures shifts in groups of species that have similar depth and temperature preferences. The project team has created new spatial data products to visualize changes in species distributions. Changes were evaluated both historically, using trawl survey data, and in the future, using cutting-edge high-resolution climate models for the U.S. Northeast Shelf. The project team produced a time series of movies and static maps, illustrating temporal changes in distributions of individual species and species groups for past, contemporary, and future time periods. These results are designed to be useful to fisheries managers, spatial planners, and the wider community of stakeholders in understanding and planning for potential climate-induced changes to valuable fisheries and the ecosystem in this region. The project was completed in two phases. During the first phase, the project team classified almost seventy species associated with the seafloor into four distinct groups, or assemblages, based on oceanographic characteristics from the spring and fall Northeast Fisheries Science Center (NEFSC) bottom trawl surveys (http://www.nefsc.noaa.gov). Because the oceanographic and habitat characteristics are so different between the Gulf of Maine (the northern Northeast Shelf) and the Mid-Atlantic Bight and Georges Bank (the southern Northeast Shelf), the species groups were examined separately in these two regions. Oceanographic data on depth and surface and bottom temperature proved to be key in distinguishing the groups in each region. Observed shifts in species distributions were compared with shifts in temperature to determine whether consistent responses to climate change were visible within the species groups. There were distinct differences in shifts in the assemblages of species in each region. Species associated with warmer, shallower waters in the Mid- Atlantic Bight and Georges Bank exhibited a strong northward shift, tracking shifts in temperature bands along the shelf. In contrast, species in the Gulf of Maine were shifting to the southwest, possibly tracking the cooler bottom waters on the shelf and in deeper basins in this area of the Gulf. Additionally, species in the Gulf of Maine associated with cooler and deeper waters tended to shift deeper, taking advantage of the variable bottom topography in this region. In the second phase of the project, a high-resolution climate model was used to model future species distribution shifts in the next 20-80 years. In general, species that are currently distributed in the south of the U.S. Northeast Shelf in the Mid-Atlantic Bight and Georges Bank were found to shift northward and many species currently found in the Gulf of Maine did not have access to habitat with a suitable temperature in the future. This may have important impacts on the viability of species currently inhabiting the Gulf of Maine and their ability to maintain robust populations in the future. This will also translate into impacts on the commercial fisheries in this region. Overall, it is understood that, given climate change, there will be some species that will be winners and others that will be losers. What is harder to predict is how these dynamics will unfold on the U.S. Northeast Shelf, especially given the extreme warming predicted by global climate models. Understanding how species have shifted over the past decades in combination with future temperature predictions from climate models can help identify the potential impacts of climate change on vulnerable fish species. Additionally, current and potential biomass hotspots and areas of high fish biodiversity can be identified to help highlight the implications for fishermen and communities that depend on fisheries resources. Together these results provide critical information for the development of spatial management strategies in response to climate change.

Major Findings Figure 1 The Northeast U.S. Shelf illustrating the southern region: the Mid-Atlantic Bight and Georges Bank, and northern region: the Gulf of Maine with shaded bathymetry (meters depth). Using a combination of temperature and habitat variables sampled on the U.S. Northeast Shelf the project defined groups of species based on preferred temperatures and depths and explored historical distribution shifts. Exploring distribution shifts between the species groups on a regional basis illustrated different patterns between the Gulf of Maine, a region with variable bottom topography and complex currents, and the Mid- Atlantic Bight and Georges Bank in the south, a region with more uniform depths. In the Gulf of Maine, the centers of distribution of many species shifted to the southwest, possibly tracking cooler bottom temperatures in the southwestern Gulf. Species associated with cooler and deeper waters tended to shift to deeper waters. Along the Mid-Atlantic Bight and Georges Bank, the centers of biomass of many species shifted to the northeast, tracking shifts in temperature bands. In this region, species associated with shallow, warmer waters shifted northward at the greatest rates, generally staying in shallower waters. Species with current centers of distribution on the Mid- Atlantic Bight or Georges Bank may be future climate winners because they can shift northward or deeper. Species that are currently distributed in the Gulf of Maine seem to be climate losers on the Northeast Shelf because areas with suitable temperatures in the future may not be available. Potential future shifts will mean major changes in the species composition along the U.S. Northeast Shelf. Fishing communities will need to adapt to these new conditions by switching their targeted species or traveling further to maintain viable fisheries. Introduction At a range of spatial scales, marine species worldwide are already feeling the effects of global climate change due to increasing global temperatures, altered weather patterns, changes in sea level, circulation patterns, nutrient loads [1, 2]. When possible, species may respond to climate change by shifting their distributions to regions with more favorable conditions or by adapting to the new conditions in a given region. While there is consensus among researchers that climate change affects species, it is not clear that all species will be negatively impacted. There has recently been a focus on climate winners and losers [3]. This is the concept that the abundance and distribution of some species or species groups may remain stable or expand with changes in climate whereas others may decline in abundance and distribution. While it is appreciated that some species may do better than others under climate change, how such dynamics are realized is not certain, especially given the complex interplay of changing species interactions and fishing patterns. Despite this sort of complexity, understanding changes in the availability of areas with suitable temperatures will help clarify spatial shifts in species distributions. The Northeast shelf is a highly productive and temperate system that is strongly influenced by the tides, the Gulf Stream, and gyre circulation (Figure 1). Due to the high primary productivity in the region and the fact that the Northeast shelf is a boundary ecosystem between warm and cold temperate regions, there is a diverse array of fish and invertebrates that are supported, many of which are commercially important. With complex biotic, environmental, and anthropogenic forces at play, it is critical to gain a better understanding of the interactions between species, the effects of 2

fishing pressure, and to understand the role of climate change in shifting species and community distributions. To account for this complexity, The Nature Conservancy (www.nature.org), in partnership with the Northeast Fisheries Science Center (www.nefsc.noaa.gov), undertook a project to explore the historical, current, and future distributions of species associated with the seafloor on the U.S. Northeast Shelf with respect to climatic changes. The project was carried out over two years and consisted of two phases. The first phase focused on the distributions of demersal species over the past four decades using the NEFSC bottom trawl survey data. A key feature of this analysis was that the project team defined groups of species described by habitat and oceanographic conditions sampled in the survey. The team explored how these species groups, or assemblages, had shifted spatially over the trawl survey time period and whether the groups tracked shifts in temperature. In the second phase, a high-resolution climate model was used to project the distributions of the species assemblages and individual species distributions to understand the future impacts of climate change on vulnerable fish species. The products from both phases consisted of a series of static maps, distribution movies, and supporting metadata, which can be accessed through the NEFSC Ecosystem Assessment webpage, The Nature Conservancy s Conservation Gateway, and the Northeast Ocean Data Portal: www.nefsc.noaa.gov/ecosys/spatial-analyses https://www.conservationgateway.org http://northeastoceandata.org Project Methods & Results PHASE 1 Exploring how groups of species with similar oceanographic preferences have responded to historical climate change on the U.S. Northeast Shelf 1 1 A more detailed methodological description and results from the analyses conducted in Phase I can be found in Kleisner KM, et al. (2016) the effects of subregional climate velocity on the distribution and spatial extent of marine species assemblages. Plos One. Overview Since 1968, the National Oceanographic and Atmospheric Administration (NOAA) Northeast Fishery Science Center (NEFSC) has consistently carried out a multispecies bottom trawl survey every spring and fall. Approximately 350-400 stations are sampled during each cruise using a stratified random design. The survey was implemented to meet several objectives: (1) to monitor trends in abundance, biomass, and recruitment, (2) to monitor the geographic distribution of species, (3) to collect oceanographic and environmental data, (4) to monitor changes in life history traits (e.g. trends in growth, longevity, mortality, maturation, and food habits), and (5) to monitor ecosystem changes. With respect to (3), water temperature and salinity, depth, and location are taken at each tow station. This simultaneous collection of biological and environmental data allows the determination of relationships between species and the environment. The project team selected approximately seventy of the most commonly observed species from the bottom trawl surveys. These species represented forty-three families from a wide range of species groups including flatfish, cod and hake, skates, and squids and other invertebrates. Defining species assemblages The key motivation for exploring species groups, or assemblages of species, was to determine whether some species exhibit similar distribution shifts given changes in temperature [4]. The species groups were defined based on temperature and depth using statistical clustering techniques. The species grouped into four spatially distinct assemblages per region and season characterized by species that persistently cluster together over time in each season (Table 1). There was a clear gradation in depth, and to a lesser degree bottom temperature, between the groups. Assemblages were numbered 1 to 4 to reflect groups of species associated with progressively deeper and cooler waters. In general, the shallow water species group (Table 1: Assemblage 1) in both the Gulf of Maine and the Mid-Atlantic Bight/Georges Bank consisted of shallow water demersal species generally associated with warmer bottom and surface temperatures. These are species such as alewife and bullnose stingray that are found in coastal and/or protected waters such as bays and estuaries. Additionally, in the Mid-Atlantic Bight/Georges Bank, the Assemblage 1 consisted of 3

some reef-based species such as banded drum and spiny butterfly rays. The second species group (Table 1: Assemblage 2) consisted of mid-shallow water, midand higher trophic levels species such as American shad, which are generally found in coastal waters, but with the ability to move between shallower and deeper waters. The third species group (Table 1: Assemblage 3) consisted of mid-deep water, demersal, higher trophic level species such as monkfish and barndoor skate, which are found over soft bottom habitat. This group Table 1 Description of species assemblages defined for the Gulf of Maine and Mid-Atlantic Bight/ Georges Bank regions from the fall bottom trawl survey. 4

inhabits deeper waters in the Gulf of Maine and is found along the shelf edge along the Mid-Atlantic Bight/Georges Bank region. The fourth species group (Table 1: Assemblage 4) was characterized by species such as blackbelly rosefish, which are associated with the deepest water and coldest bottom temperatures. Exploring observed shifts In order to explore observed shifts in species distributions over the time series, the project team quantified the distribution of the species in the first decade of the survey (1968 1977) and the most recent decade (2004 2013). The average latitude and longitude weighted by biomass was used to calculate the center of the distribution of each species. Then between the centers of distribution were calculated for each species in each region, seasonally. Figure 2 illustrates the average bearing and direction of movement of the center of the distributions of each of the species sampled by the bottom trawl survey in the fall. Species distributed Figure 2 Location of the centers of biomass (latitude and longitude) in the first decade (1968 1979) and the most recent decade (2002 2013) for species in the northern and southern Northeast Shelf regions. Direction of lines indicates bearing between the centers of biomass. 5

Figure 3 Observed versus predicted shifts in depth (upper panels) and latitude (lower panels) from 1968 to 2013 for species within assemblages in the northern and southern Northeast Shelf regions. along the Mid-Atlantic/Georges Bank region tended to have shifted to the northeast, possibly in an attempt to maintain preferred temperatures. In contrast, in the Gulf of Maine, the dominant direction of movement was southwest. Species shifting to the southwest may be attracted to cooler bottom waters in the southwest Gulf of Maine, a region that has remained cooler than other areas of the Gulf. Exploring predicted shifts under climate change The team also explored whether observed species shifts in latitude and depth were tracking predicted shifts in temperature bands [5]. Comparing the observed shift with the predicted shifts for each species allowed the team to determine whether there were any differences in terms of shifts in depth or latitude between species groups in the Gulf of Maine and Mid-Atlantic Bight/ Georges Bank regions. In the Mid-Atlantic Bight/Georges Bank region latitudinal shifts were more pronounced than shifts in depth (Figure 3). Species in assemblage 1, associated with warmer bottom temperatures and shallower waters, demonstrated the strongest northward shifts. 6

This shift to the north in this region makes sense as the bottom topography along the Mid-Atlantic Bight and Georges Bank is fairly homogeneous and there are few constraints to northward movement along the shelf. In the Gulf of Maine, shifts in depth were very pronounced, with no real relationship with latitudinal shifts (Figure 3). In general, species associated with cooler bottom temperatures and deeper waters tended to shift deeper. The many deep basins in the Gulf of Maine region are likely providing temperature refuges for species that are able to shift to deeper waters. Additionally, species in assemblage 1, associated with warmer bottom temperatures and shallower waters, tended to shift to shallower depths. This reflects the shifts to the southwest illustrated in Figure 2, which were likely driven by the cooler pockets of bottom water in the southwest Gulf of Maine. PHASE 2 Projecting future species distributions on the U.S. Northeast Shelf 2 The most recent Intergovernmental Panel on Climate Change (IPCC) assessment of projected global and regional ocean temperature change is based on global climate models that have relatively coarse (~100 km) ocean resolutions. At this coarse resolution, the Gulf Stream position is misrepresented in the models, resulting in climate projections that are cooler than what might be anticipated in the future. Overview Recently, the National Oceanographic and Atmospheric Administration (NOAA) Geophysical Fluid Dynamics Laboratory (GFDL) developed a new high-resolution (~10 km) climate model 2. This model more accurately depicts the position of major ocean currents like the Gulf Stream, reducing uncertainty in future temperature predictions [6]. This represents a huge advancement in global climate modeling. Unfortunately, however, the new high-resolution model indicates that ocean temperatures on the U.S. Northeast Shelf are likely to warm two times faster than what the coarser models had predicted. While projecting species distributions is associated with high uncertainty due to unaccounted for species interactions, other complex ecosystem effects, and uncertainty in climate forecasts, such projections can be useful as scenarios for informing adaptation policies and management decisions. Using the more refined future (80-year) projections of bottom and surface temperature across the NES region from the high-resolution climate model, the project team made future projections of the distributions of individual species on the U.S. Northeast Shelf. The team explored the idea that some species may be able to adapt to climate change within the region better than others. Humans will likely have to adapt and modify their behaviors in response to species distribution shifts in the future. Exploring future shifts in species distributions Using predictive models, the project team quantified the relationship between biomass and environmental variables measured on the bottom trawl surveys (depth, bottom and surface temperature). Then, the future biomass was predicted using the projected bottom and surface temperatures from the high-resolution climate model as inputs. These models are very simple and cannot account for many of the other possible drivers of species distribution shifts (e.g., fishing pressure, species interactions, habitat modification). However, given the extreme temperature change predicted for this region [6] and the contemporary importance of temperature effects on species in the region [7], it is likely that temperature changes will be one of the main drivers of species distribution shifts on the U.S. Northeast Shelf. Because of the models limitations, their output should not be considered to be a prediction of future biomass. Instead, they provide an indication of the potential for the presence of suitable thermal conditions over the historical (observed) time period and in the future based on temperature changes. We refer to the presence of suitable thermal conditions as thermal habitat. For each species, maps and movies were made annually for the observed time period (1968 2013) and projections over 80 years illustrating these changes in thermal habitat: www.nefsc.noaa.gov/ecosys/spatial-analyses In general, species that currently have a more southerly distribution tended to show stable or increasing spatial ranges (Figure 4). This likely reflects the fact that they are able to shift northward or deeper to maintain preferred thermal habitat. Conversely, species that currently have a more northerly distribution tended to show decreases in thermal habitat over the survey region (Figure 4). This likely reflects the fact that temperatures in the Gulf of Maine will become too warm and inhospitable for these species. It is important to note that species with distributions in U.S. waters that are currently at their southern limits (e.g. Atlantic cod), may find suitable thermal habitat in more northern waters or off the shelf. Therefore, this study 7

can only determine whether areas within the survey region are likely to hold potential as suitable thermal habitat zones. These changes in thermal habitat can be shown on a map for current and future time periods. Figure 4 Percent change in suitable thermal habitat (positive: more habitat; negative: less habitat) from the modeled 1991 2013 period to the future 60 80 year projected period for fall. Species denoted with an (*) had positive percent changes greater than 500%. Colors indicate species whose distribution is currently centered in the Gulf of Maine (orange) or along the Mid-Atlantic Bight and Georges Bank (purple). 8

Figure 5 Comparison of the modeled historical and future distributions of suitable thermal habitat in the fall (red: more habitat; blue: less habitat) for species with a more northern distribution (upper rows: Atlantic cod and red hake) and more southern distributions (lower rows: smooth dogfish and Atlantic croaker). In Figure 5 we provide an example for two species that currently have a more southerly distribution (e.g. Atlantic croaker and smooth dogfish) and two species with a more northerly distribution (e.g. Atlantic cod and red hake). Despite the modeling limitations associated with global climate model outputs and forecasting species distributions, the results illustrate some important trends. First, there will potentially be some major changes in the complex of species occupying different regions of the U.S. Northeast Shelf. Along the Mid- Atlantic Bight, shifting distributions of traditionally harvested species alter patterns of availability to local fishing communities. This may impose economic impacts as a result of lost access to stocks managed with species-specific quotas, and rising fuel and travel costs. In some cases, fishermen will need to adapt to altered ecosystems with new subtropicaltemperate species. In contrast, the Gulf of Maine is likely to see new species that currently dominate more southerly waters along the Mid-Atlantic Bight. In some cases, species that currently occupy the Gulf of Maine may be concentrated within deeper pockets as temperatures change, resulting in increased vulnerability to fishing activity, or may be pushed out of the region altogether. Further, species may shift from one management jurisdiction to another, or occur in multiple jurisdictions. When these changes straddle fishery management boundaries, increased collaboration will be needed among governing bodies. Collectively, these changes will result in important ecological, economic, social, and natural resource management challenges throughout the region. 9

Project Takeaways Historical perspective Using a combination of temperature and habitat variables sampled on the U.S. Northeast Shelf the project defined groups of species based on preferred temperatures and depths and explored historical distribution shifts. Exploring distribution shifts between the species groups on a regional basis illustrated different patterns between the Gulf of Maine, a region with variable bottom topography and complex currents, and the Mid- Atlantic Bight and Georges Bank in the south, a region with more uniform depths. In the Gulf of Maine, the centers of distribution of many species shifted to the southwest, possibly tracking cooler bottom temperatures in the southwestern Gulf. Species associated with cooler and deeper waters tended to shift to deeper waters. Along the Mid-Atlantic Bight and Georges Bank, the centers of biomass of many species shifted to the northeast, tracking shifts in temperature bands. In this region, species associated with shallow, warmer waters shifted northward at the greatest rates, generally staying in shallower waters. Future perspective There will potentially be some major changes in the complex of species occupying different regions of the U.S. Northeast Shelf. Species currently distributed on the Mid-Atlantic Bight or Georges Bank may be future climate winners because they can shift northward or deeper. Species whose distribution is currently centered in the Gulf of Maine are likely to be climate losers on the Northeast Shelf because areas with suitable temperatures are may not be available. Along the Mid-Atlantic Bight, changes in the availability of traditionally harvested species may impose economic impacts as a result of lost access to stocks managed with species-specific quotas, and rising fuel and travel costs. Species that currently dominate more southerly waters along the Mid-Atlantic Bight may shift into the Gulf of Maine. Deep pockets in the Gulf of Maine become temperature refuges for species that currently occupy the region. Concentration of species may result in increased vulnerability to fishing activity. Some species in the Gulf of Maine that cannot find suitable temperatures or temperature refuges may be pushed out of the region altogether. Shifting species distributions will require increased collaboration among governing bodies. Fishing communities will need to adapt to new conditions by switching their targeted species or traveling further to maintain viable fisheries. References 1. Walther GR, et al. (2002) Ecological responses to recent climate change. Nature 416(6879): 389-395. 2. Stock CA, et al. (2011) On the use of IPCC-class models to assess the impact of climate on Living Marine Resources. Progress in Oceanography 88: 1-27. 3. Glantz MH (1995) Assessing the impacts of climate: The issue of winners and losers in a global climate change context. Studies in Environmental Science 65: 41-54. 5. Pinsky ML, Worm B, Fogarty MJ, Sarmiento JL, & Levin SA (2013) Marine taxa track local climate velocities. Science 341(6151):1239-1242. 6. Saba VS, et al. (2015) Enhanced warming of the Northwest Atlantic Ocean under climate change. Journal of Geophysical Research: Oceans 120. 7. Fogarty MJ, Incze L, Hayhoe K, Mountain D, & Manning J (2008) Potential climate change impacts on Atlantic cod (Gadus morhua) off the northeastern USA. Mitigation and Adaptation Strategies for Global Change 13: 453-466. 4. Kleisner KM, et al. (2016) The effects of sub-regional climate velocity on the distribution and spatial extent of marine species assemblages. Plos One 11(2): e0149220. 10