Literature DB >> 35437402

Fine-scale abundance of rocky shore macroalgae species with distribution limits in NW Iberia in 2020/2021.

Joana Pereira1, Catia Monteiro1, Rui Seabra1, Fernando P Lima1.   

Abstract

Background: Climate change has been increasing at an unprecedented rate in the last decades. Global warming has been causing a variety of impacts in marine ecosystems, including shifts in the geographical ranges of species. The north-western Iberian Peninsula coast is particularly interesting to study distribution shifts as it features a strong latitude thermal gradient, establishing a biogeographical transitional region where several cold- and warm-adapted species have their equatorward or poleward distributions. In the early 2000s, it appeared that, while warm-water species were already responding to warming, cold-water species did not display a coherent response. It is now necessary to gather up-to-date data on the distribution of the same group of species to understand if current patterns of change confirm or deny those observed back then, which may give us important clues about the mechanisms setting species limits in the area. New information: This study provides a fine-scale description of the occurrence of intertidal macroalgae species in the rocky shores of the north-western Iberian coast. Specifically, the spatial distribution and semi-quantitative abundance of 34 native and invasive species were assessed at 70 wave-exposed locations. This included 19 species of cold-water affinity, 10 species of warm-water affinity and five neutral species. When contrasted with historical observations, these new data can be used to quantify and map biodiversity change in the region, as well as help understanding the mechanisms constraining species distributions. Joana Pereira, Catia Monteiro, Rui Seabra, Fernando P. Lima.

Entities:  

Keywords:  distribution; intertidal; macroalgae; north-western Iberia; rocky shores

Year:  2022        PMID: 35437402      PMCID: PMC9005454          DOI: 10.3897/BDJ.10.e80798

Source DB:  PubMed          Journal:  Biodivers Data J        ISSN: 1314-2828


Introduction

Climate has been changing at unprecedented rates (IPCC 2021). Amongst the most pervasive effects of climate change have been shifts in the geographical distribution of species (Parmesan and Yohe 2003), generally tracking isotherms towards the poles (Lenoir et al. 2020). Intertidal species are considered sensitive indicators of climate change (Southward et al. 1995), as they are particularly vulnerable to environmental extremes, including high temperatures (Sorte et al. 2016, Zamir et al. 2018). The North-western Iberian Peninsula coast features a strong latitude thermal gradient, establishing a biogeographical transitional region where several cold- and warm-adapted species have their equatorward or poleward distribution limits (Fischer-Piette 1959, Fischer-Piette and Gaillard 1959, Fischer-Piette 1963, Ardré 1970, Lima et al. 2007, Araújo et al. 2009) and where shifts in those limits have been described since the 1950s (Fischer-Piette and Forest 1951, Fischer-Piette 1957, Fischer-Piette and Prenant 1957, Fischer-Piette 1960, Berke et al. 2010, Wethey et al. 2011, Sousa et al. 2012, Rubal et al. 2013). In the summer, the latitudinal thermal gradient is further intensified by the cooling effect of the Canary upwelling system, stronger in the northern portion of the coast. Recent studies suggest that this cooling may be, at least partially, buffering coastal ecosystems from decades of global warming (Seabra et al. 2019), but the extent to which this is actually happening has not yet been verified in the field. Anticipating a prevalence of distributional shifts towards the north, in the early 2000s Lima and colleagues conducted several surveys in the area (Lima et al. 2007, Pereira et al. 2021c), finding that, while all warm-water species that were changing were expanding their range northwards, cold-water species showed no particular shifting trend as the number that retreated north or expanded south was the same. It seemed, at the time, that warm-water species were already responding to warming, but the same could not be said about cold-water species (Lima et al. 2007). Although it is likely that communities kept changing since those observations in the early 2000s (Harley et al. 2012), detailed up-to-date information is not available. Budgetary constraints and logistical limitations inherent to field surveys mean that data are often outdated or poor in details (Casado-Amezúa et al. 2019). Most recent surveys in the area lack the necessary taxonomic coverage (Araújo et al. 2011, Assis et al. 2017), geographical range (Piñeiro-Corbeira et al. 2016) or spatial resolution (Meneghesso 2020) to either pinpoint the exact distribution limits of those species or to evaluate changes in abundance towards those limits. It is essential to gather fresh data on the distribution of the same group of species studied more than one decade ago to understand if current patterns of change confirm or deny those observed back then. Determining the generalisation of those observations is important, as they may give us clues on the mechanisms constraining species distributions (which may even differ between warm and cool range edges, see Paquette and Hargreaves 2021). In an effort to reduce this knowledge gap, this study aimed at re-assessing the abundance and the distribution limits of 34 native and invasive species of rocky shore macroalgae species with high spatial accuracy, at 70 wave-exposed locations along the north-western coast of the Iberian Peninsula.

Sampling methods

Study extent

Data were collected between autumn 2020 and summer 2021. Sampling was carried out at 70 wave-exposed rocky shore locations along the north-western Iberian coast, covering three major rocky stretches of shoreline in the regions of Galicia, northern Portugal and central Portugal (Table 1, Table 2, Fig. 1, Fig. 2). In Galicia, we sampled the locations of Cabo Touriñán, Corveiro, Quenxe, Ximprón, Punta Outeiriño, Corrubedo, O Touro, Prado, Faro Vello de Silleiro, Oia and Fedorento. In northern Portugal, we surveyed the locations of Moledo, Vila Praia de Âncora, Afife, Montedor, Forte da Vigia, Praia Norte, Cabedelo (breakwater), Amorosa, Foz do Neiva, Rio de Moinhos, Esposende (breakwater), Ofir (southern breakwater), Pedrinhas, Apúlia, Santo André, Verde, Carvalhido, Póvoa de Varzim (), Caxinas, Forte de São João, Azurara (breakwater), Areia, Mindelo, Facho, Sampaio, Labruge, Angeiras (Maelas), Angeiras (Praia dos Barcos), Praia Central, Funtão, Pedras do Corgo, Pedras da Agudela, Memória, Cabo do Mundo, Boa Nova, Leça (Piscina das Marés), Leça (breakwater), Matosinhos (northern breakwater), Castelo do Queijo, Homem do Leme, Salgueiros, Valadares, Senhor da Pedra, Aguda, Bairro Piscatório (northern breakwater), Paramos (southern breakwater), Maceda (breakwater), Torreira (breakwater), Barra (northern breakwater), Barra (southern breakwater), Costa Nova (northern breakwater), Costa Nova (southern breakwater), Poço da Cruz (breakwater), Figueira da Foz and Buarcos. In central Portugal, the locations Figueira da Foz, Nazaré, São Martinho do Porto, Baleal and Papoa were surveyed. While most of these sites are natural rocky shores (Table 1), 17 are composed of artificial hard substrate amongst sandy beaches (Table 2). Some sites were surveyed twice.
Table 1.

Natural rocky shore sites surveyed, their coordinates and date of the survey. The coordinates were obtained from GoogleMaps imagery. Locations are listed from north to south.

ID Location Latitude Longitude Date Astronomical low tide height (m below mean sea water level)
1Cabo Touriñán 43.04423 -9.28810 24/05/2021-1.52
2Corveiro 42.90442 -9.26077 26/05/2021-1.68
3Quenxe 42.93650 -9.18958 26/05/2021-1.68
4Ximprón 42.79679 -9.14016 25/05/2021-1.63
5Punta Outeiriño 42.74564 -9.07681 25/05/2021-1.63
6Corrubedo 42.57665 -9.08985 26/06/2021-1.45
7O Touro 42.54606 -8.98397 26/06/2021-1.45
8Prado 42.15921 -8.81940 27/05/2021-1.62
9Faro Vello de Silleiro 42.11185 -8.89945 27/05/2021-1.62
10Oia 42.00199 -8.87770 28/05/2021-1.49
11Fedorento 41.91017 -8.87801 28/05/2021-1.48
12Moledo 41.83815 -8.87491 19/10/2020-1.69
12Moledo 41.83908 -8.87529 25/06/2021-1.43
13Vila Praia de Âncora 41.81940 -8.87205 17/12/2020-1.45
14Afife 41.78439 -8.87168 17/12/2020-1.69
14Afife 41.78072 -8.87014 19/10/2020-1.45
15Montedor 41.74292 -8.87591 29/01/2021-1.37
16Forte da Vigia 41.69959 -8.85507 16/11/2020-1.72
17Praia Norte 41.69983 -8.85472 16/11/2020-1.72
19Amorosa 41.64290 -8.82338 12/01/2021-1.39
20Foz do Neiva 41.61095 -8.80893 16/12/2020-1.55
21Rio de Moinhos 41.57362 -8.79846 16/12/2020-1.55
25Apúlia 41.48267 -8.77886 17/11/2020-1.62
26Santo André 41.41663 -8.78827 15/01/2021-1.42
27Verde 41.38542 -8.77433 15/01/2021-1.42
28Carvalhido 41.38149 -8.77150 30/03/2021-1.79
30Caxinas 41.36220 -8.76045 13/01/2021-1.46
31Forte de São João 41.34108 -8.75073 13/01/2021-1.46
33Areia 41.33355 -8.73993 14/01/2021-1.49
34Mindelo 41.31052 -8.74136 14/01/2021-1.49
35Facho 41.29241 -8.73419 15/12/2020-1.58
36Sampaio 41.27956 -8.72914 15/12/2020-1.58
37Labruge 41.27309 -8.72900 16/01/2021-1.32
38Angeiras (Maelas) 41.26615 -8.72829 31/03/2021-1.68
39Angeiras (Praia dos Barcos) 41.26510 -8.72818 16/01/2021-1.32
40Praia Central 41.26187 -8.72686 31/01/2021-1.48
41Funtão 41.26041 -8.72494 15/11/2020-1.66
42Pedras do Corgo 41.24931 -8.72591 15/11/2020-1.66
43Pedras da Agudela 41.24163 -8.72795 14/11/2020-1.55
44Memória 41.23528 -8.72433 17/10/2020-1.71
45Cabo do Mundo 41.22115 -8.71577 17/10/2020-1.71
46Boa Nova 41.20458 -8.71553 16/10/2020-1.59
47Leça (Piscina das Marés) 41.19231 -8.70742 16/10/2020-1.59
50Castelo do Queijo 41.16746 -8.69016 15/10/2020-1.38
50Castelo do Queijo 41.16722 -8.69020 23/06/2021-1.35
51Homem do Leme 41.15903 -8.68538 14/12/2020-1.54
51Homem do Leme 41.15903 -8.68538 14/02/2021-1.37
52Salgueiros 41.12148 -8.66652 18/11/2020-1.45
53Valadares 41.08964 -8.65700 18/11/2020-1.46
54Senhor da Pedra 41.06894 -8.65836 18/10/2020-1.76
54Senhor da Pedra 41.06846 -8.65848 24/06/2021-1.40
55Aguda 41.04554 -8.65282 18/10/2020-1.76
55Aguda 41.04613 -8.65325 24/06/2021-1.40
64Buarcos 40.17751 -8.90354 03/03/2021-1.46
65Pedrogão 39.91612 -8.95537 12/04/2021-1.31
67Nazaré 39.60384 -9.08041 01/03/2021-1.63
68São Martinho do Porto 39.51151 -9.14207 26/07/2021-1.28
69Papôa 39.37344 -9.37773 02/03/2021-1.58
70Baleal 39.37586 -9.33981 02/03/2021-1.58
Table 2.

Artificial substrate locations surveyed and their correspondent coordinates and date of the survey. The coordinates were obtained from GoogleMaps imagery. Locations are listed from north to south.

ID Location Latitude Longitude Date Astronomical low tide height (m below mean sea water level)
18Cabedelo (breakwater) 41.67923 -9.83669 15/03/2021-1.35
22Esposende (breakwater) 41.54149 -8.79361 28/03/2021-1.65
23Ofir (southern breakwater) 41.51551 -8.78768 28/03/2021-1.65
24Pedrinhas 41.50590 -8.78829 17/11/2020-1.62
29Póvoa de Varzim (marina) 41.37615 -8.76433 28/03/2021-1.65
32Azurara (breakwater) 41.33919 -8.74709 30/03/2021-1.79
48Leça (breakwater) 41.18622 -8.70760 31/03/2021-1.68
49Matosinhos (northern breakwater) 41.17800 -8.69908 23/06/2021-1.35
56Bairro Piscatório (northern breakwater) 40.99809 -8.64944 12/03/2021-1.37
57Paramos (southern breakwater) 40.97362 -8.65141 12/03/2021-1.37
58Maceda (breakwater) 40.93121 -8.66139 12/03/2021-1.37
59Barra (northern breakwater) 40.64102 -8.75212 14/03/2021-1.44
60Barra (southern breakwater) 40.62783 -8.75108 14/03/2021-1.44
61Costa Nova (northern breakwater) 40.61955 -8.75398 14/03/2021-1.44
62Costa Nova (southern breakwater) 40.61949 -8.74819 14/04/2021-1.24
63Poço da Cruz (breakwater) 40.48955 -8.79457 13/03/2021-1.43
66Figueira da Foz (marina) 40.14684 -8.86726 13/03/2021-1.41
Figure 1.

Study locations along the north-western Iberia coast visited in the years of 2020 and 2021. Location details and sampling dates can be found in Table 1 and Table 2.

Figure 2.

Examples of shores surveyed in the present study. A - Oia, in Galicia, B – Moledo, in northern Portugal and C – Cabedelo (breakwater), an artificial site in northern Portugal. D – Papôa, in central Portugal.

For this work, we selected 34 intertidal macroalgae species to study possible changes in their abundance close to their geographic range limit (Suppl. material 1). We chose conspicuous macro-algae species as they are not only easy to observe and identify, but also less likely to be overlooked. This is important because reliable absence data is as essential as reliable presence data when assessing distribution change through time. The choice of species followed Lima et al. (2007) in order to obtain a comparable dataset. Briefly, we selected species that either have their absolute range limit or a distribution gap within or near the study area (Lima et al. 2007). We classified the species as warm-water, cold-water or neutral, based on how their Species Temperature Index (STI) compares with the median temperature of all surveyed sites in NW Iberia. STI was calculated using the median sea surface temperature (SST) of all coastal sites where the species is present in the North Atlantic Ocean, obtained by averaging 40 years of daily SST (1982–2021) from NOAA 1/4 arc-degree Daily Optimum Interpolation SST version 2, dOISST.v.2 (Banzon et al. 2016). This yielded a list of 19 species of cold-water affinity (macroalgae for which the species STI is lower than the median temperature in the study area), 10 species of warm-water affinity (macroalgae for which the STI is lower than the median temperature of the study area and five neutral species (with STI higher than the median temperature of some sites, but lower than others). From these, 30 are considered native species while four are invasive species.

Sampling description

All locations were surveyed by a two-people team during spring low tides (the average low tide level was 1.52 +/- 0.14 m below mean sea water level, Fig. 3, Table 1, Table 2). Two locations were surveyed per day, one while the tide was still going out and another when the tide was already starting to rise. Each location was thoroughly surveyed for at least 60 minutes, except for most breakwaters which, owing to their relatively small area, were typically surveyed in less time. A semi-quantitative estimation of abundance was assigned to each selected species. We used a modified version of the scale established by Crisp and Southward (1958) — SACFOR, where abundances were encoded from 6 to 0 (where 6 means Superabundant; 5, Abundant; 4, Common; 3, Frequent; 2, Occasional; 1, Rare; and 0, not found).
Figure 3.

Two-person team recording SACFOR abundances at Aguda on 18/10/2020.

Additionally, a herbarium was created with one specimen preserved per observed species per site, when feasible (Fig. 4). The algae collected were placed on drawing paper together with information on the species name, the location of collection, date and the sample collectors. Specimens were covered by non-adherent paper and placed between journal paper to dry. All specimens were piled and a weight was added on top so that the pressure helped to flatten them and stick them to the paper. Photos of each specimen were taken to duplicate the information in digital support. These photos were taken with a Canon EOS 6D camera fitted with a 28-80 mm objective at a fixed distance (55 cm), without zoom and with a €1 coin to serve as scale. Digital photos are available as an occurrence daset in GBIF (Pereira et al. 2021a), described below in Data Resources.
Figure 4.

Representation of steps taken in the creation of herbarium: A - cleaning of specimens; B - identification of specimens, their collection location, date and collectors; C - photographing specimens.

Quality control

In addition to AlgaeBase (Guiry and Guiry 2021), authoritative identification guides and keys for the Eastern Atlantic and Mediterranean were used (Dixon and Irvine 1977, Hiscock 1979, Chapman and Goudey 1983, Irvine 1983, Hiscock 1986, Bárbara and Cremades 1987, Christensen 1987, Fletcher 1987, Burrows 1991, Cabioc'h et al. 1992, Maggs and Hommersand 1993, Irvine and Chamberlain 1994, Molenaar et al. 1996, Stuart et al. 1999, Brodie and Irvine 2003, Faes and Viejo 2003, Aziza et al. 2008, Araújo et al. 2009, Bárbara 2009, Vieira et al. 2010, Araújo et al. 2011, Edwards et al. 2012, Bárbara 2013, Bunker et al. 2017, Benita et al. 2018, Poza et al. 2019). All scientific names were standardised against the WoRMS - The World Register of Marine Species using the Taxon Match tool accessed on 07-07-2021 (WoRMS Editorial Board 2021).

Step description

The steps that led to the final release of the dataset were as follows: (1) In-situ identification of species and attribution of a semi-quantitative abundance SACFOR score; (2) collection of specimens; (3) preservation of specimens in a herbarium; (4) photographing of each specimen as to duplicate the information in digital support; (5) standardisation of taxonomy against the World Register of Marine Species; (6) exporting of data as a DarwinCore Archive and (7) generation of dataset-level metadata.

Geographic coverage

Description

Sampling was done along three major rocky stretches of coast in north-western Iberia, covering the regions of Galicia, northern Portugal and central Portugal.

Coordinates

39.37344 and 43.04422 Latitude; -8.64943 and -9.37772 Longitude.

Taxonomic coverage

A total of 34 algae species were surveyed (19 , 13 and 2 ): , , , , , , , , , , , , , , , , , , , , , Padina pavonica, , , , , , a, , , , , and . When it was not possible to discern between and (at the juvenile stage), specimens were classified at the genus level, sp. Full taxonomic description is presented on Suppl. material 1.

Temporal coverage

Data range: 2020-10-15 – 2021-7-26.

Usage licence

Usage licence

Open Data Commons Attribution License

IP rights notes

Data users are free to share, create and adapt the dataset as long as they adequately attribute (cite) this work.

Data resources

Data package title

A survey of intertidal macroalgae species distribution along the north-western Iberian coast in 2020/2021 (occurrence/abundance/herbarium specimens)

Resource link

http://ipt.gbif.pt/ipt/resource?r=2021_iberianpeninsula; https://doi.org/10.15468/9t2gxy

Alternative identifiers

https://doi.org/10.15468/247z4g; http://ipt.gbif.pt/ipt/resource?r=herbarium

Number of data sets

2

Data set 1.

Data set name

Intertidal macroalgae species distribution along the north-western Iberian coast in 2020/2021

Data format

Darwin Core archive

Number of columns

37

Download URL

https://www.gbif.org/dataset/c1e31227-6595-4797-b75a-d9d9f75e4cca

Description

The data presented in this paper results from visual surveys done along the north-western Iberian rocky intertidal in 2020 and 2021, focusing on 34 macroalgae species. The dataset published in GBIF has the structure of a Sampling event dataset with two data subsets: Events (Core) and Associated occurrences. These data have been published (Pereira et al. 2021b) as a Darwin Core Archive (DwCA), which is a standardised format for sharing biodiversity data (Wieczorek et al. 2012). The Sampling Event (Core) contains 77 records (eventID). The extension data (Associated Occurrences) sheet has 2632 occurrences.

Data set 2.

Herbarium collection of intertidal macroalgae biodiversity along the north-western Iberian coast in 2020/2021 29 https://www.gbif.org/dataset/e9543008-b26d-458e-b334-a201c5c3b7e5 This collection comprises 378 herbarium specimens preserved, dried and stored at CIBIO and 378 photos of these specimens stored digitally (Pereira et al. 2021a). These herbarium specimens were collected while surveying the occurrence and abundance of macroalgae species in north and central Portugal and northwest Spain.

Additional information

A total of 34 macroalgae species were surveyed: 19 , 13 and two (Pereira et al. 2021b). More taxonomic information per species is presented in Suppl. material 1. Taxonomic and biogeographic information Taxonomic and biogeographic data List of species surveyed, scientific name ID from the World Register of Marine Species (WoRMS) and taxonomic ranks. File: oo_635548.txt
RankScientific Name
phylum Ochrophyta
phylum Rhodophyta
phylum Chlorophyta
Data set 1.
Column labelColumn description
eventIDUnique identifier associated with an event.
samplingProtocolSampling method used during the event.
samplingEffortDescription of effort during the sampling event.
eventDateThe date of the event.
yearThe year of the event.
monthThe month of the event.
dayThe day of the event.
countryCountry where the event took place.
countryCodeThe unique code of the country where the event took place.
LocalityA description commonly associated with the sampling place.
locationIDAn identifier for the location information from Geonames.
decimalLatitudeThe geographical latitude of the event.
decimalLongitudeThe geographical longitude of the event.
geodeticDatumThe geodetic datum upon which the geographical coordinates are based.
coordinatePrecisionThe precision of the coordinates.
coordinateUncertaintyInMetresThe uncertainty of the coordinates, in metres.
typeType of dataset.
ownerInstitutionCodeIdentifier code of the owner institution.
habitatThe habitat in which the event took place.
waterBodyThe water body in which the event took place.
rightsHolderThe rights holder of the dataset.
occurrenceIDUnique identifier associated with the occurrence of a species.
basisOfRecordThe specific nature of the data record.
organismQuantityAn enumeration value for the quantity of a species.
organismQuantityTypeThe quantification scale of the quantity of a species.
occurrenceStatusA statement about the presence or absence of a species in a location.
scientificNameThe full scientific name, with authorship and date information, if known.
scientificNameIDUnique identifier of a species, obtained from WoRMS.
kingdomThe full scientific name of the kingdom in which the taxon is classified.
phylumThe full scientific name of the phylum in which the taxon is classified.
classThe full scientific name of the class in which the taxon is classified.
orderThe full scientific name of the order in which the taxon is classified.
familyThe full scientific name of the family in which the taxon is classified.
genusThe full scientific name of the genus in which the taxon is classified.
specificEpithetThe specific epithet of the species.
taxonRankThe taxonomic rank of the most specific name in scientificName.
recordedByPeople responsible for sampling the occurrence.
Data set 2.
Column labelColumn description
occurrenceIDUnique identifier associated with an occurrence.
basisofRecordThe specific nature of the data record.
eventDateThe date when the occurrence was observed.
yearThe year when the occurrence was observed.
monthThe month when the occurrence was observed.
dayThe day when the occurrence was observed.
scientificNameThe full scientific name, with authorship and date information, if known.
kingdomThe full scientific name of the kingdom in which the taxon is classified.
phylumThe full scientific name of the phylum in which the taxon is classified.
classThe full scientific name of the class in which the taxon is classified.
orderThe full scientific name of the order in which the taxon is classified.
familyThe full scientific name of the family in which the taxon is classified.
genusThe full scientific name of the genus in which the taxon is classified.
specificEpithetThe specific epithet of the species.
taxonRankThe taxonomic rank of the most specific name in scientificName.
decimalLatitudeThe geographical latitude where the occurrence was recorded.
decimalLongitudeThe geographical longitude where the occurrence was recorded.
geodeticDatumThe geodetic datum upon which the geographical coordinates are based.
coordinateUncertaintyInMetersThe uncertainty of the coordinates, in metres.
continentThe continent where the occurrence was recorded.
countryThe country where the occurrence was recorded.
countryCodeThe standard code for the country where the occurrence was recorded.
typeThe nature or genre of the resource.
associatedMediaA list (concatenated and separated) of identifiers (URI) of media associated with the Occurrence.
institutionCodeThe name (or acronym) in use by the institution having custody of the object(s) or information referred to in the record.
recordedByPeople responsible for sampling the occurrence.
establishmentMeansStatement about whether an organism or organisms have been introduced to a given place and time through the direct or indirect activity of modern humans.
preparationsA list (concatenated and separated) of preparations and preservation methods for a specimen.
rightsHolderAn organisation owning or managing rights over the resource.
  9 in total

1.  A globally coherent fingerprint of climate change impacts across natural systems.

Authors:  Camille Parmesan; Gary Yohe
Journal:  Nature       Date:  2003-01-02       Impact factor: 49.962

2.  Decadal changes in the distribution of common intertidal seaweeds in Galicia (NW Iberia).

Authors:  Cristina Piñeiro-Corbeira; Rodolfo Barreiro; Javier Cremades
Journal:  Mar Environ Res       Date:  2015-12-12       Impact factor: 3.130

3.  Long-term declines in an intertidal foundation species parallel shifts in community composition.

Authors:  Cascade J B Sorte; Victoria E Davidson; Marcus C Franklin; Kylla M Benes; Meredith M Doellman; Ron J Etter; Robyn E Hannigan; Jane Lubchenco; Bruce A Menge
Journal:  Glob Chang Biol       Date:  2016-08-01       Impact factor: 10.863

Review 4.  EFFECTS OF CLIMATE CHANGE ON GLOBAL SEAWEED COMMUNITIES.

Authors:  Christopher D G Harley; Kathryn M Anderson; Kyle W Demes; Jennifer P Jorve; Rebecca L Kordas; Theraesa A Coyle; Michael H Graham
Journal:  J Phycol       Date:  2012-09-17       Impact factor: 2.923

5.  Species better track climate warming in the oceans than on land.

Authors:  Jonathan Lenoir; Romain Bertrand; Lise Comte; Luana Bourgeaud; Tarek Hattab; Jérôme Murienne; Gaël Grenouillet
Journal:  Nat Ecol Evol       Date:  2020-05-25       Impact factor: 15.460

6.  A comprehensive assessment of the intertidal biodiversity along the Portuguese coast in the early 2000s.

Authors:  Joana Pereira; Pedro A Ribeiro; António Múrias Santos; Cátia Monteiro; Rui Seabra; Fernando P Lima
Journal:  Biodivers Data J       Date:  2021-10-08

7.  Darwin Core: an evolving community-developed biodiversity data standard.

Authors:  John Wieczorek; David Bloom; Robert Guralnick; Stan Blum; Markus Döring; Renato Giovanni; Tim Robertson; David Vieglais
Journal:  PLoS One       Date:  2012-01-06       Impact factor: 3.240

8.  Major shifts at the range edge of marine forests: the combined effects of climate changes and limited dispersal.

Authors:  J Assis; E Berecibar; B Claro; F Alberto; D Reed; P Raimondi; E A Serrão
Journal:  Sci Rep       Date:  2017-03-09       Impact factor: 4.379

  9 in total

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