Abstract
Alexandrium fundyense is the toxic marine dinoflagellate responsible for “red tide” events in temperate and sub-arctic waters worldwide. In the Gulf of Maine (GOM) and Bay of Fundy in the Northwest Atlantic, blooms of A. fundyense recur annually, and are associated with major health and ecosystem impacts. In this region, microsatellite markers have been used to investigate genetic structure and gene flow; however, the loci currently available for this species were isolated from populations from Japan and the North Sea, and only a subset are suitable for the analysis of A. fundyense populations in the Northwest Atlantic. To facilitate future studies of A. fundyense blooms, both in this region and globally, we isolated and characterized 17 polymorphic microsatellite loci from 31 isolates collected from the GOM and from the Nauset Marsh System, an estuary on Cape Cod, MA, USA. These loci yielded between two and 15 alleles per locus, with an average of 7.1. Gene diversities ranged from 0.297 to 0.952. We then analyzed these same 31 isolates using previously published markers for comparison. We determined the new markers are sufficiently variable and better suited for the investigation of genetic structure, bloom dynamics, and diversity in the Northwest Atlantic.
Key index words: Alexandrium fundyense, dinoflagellate, harmful algal bloom, microsatellite, Paralytic Shellfish Poisoning
INTRODUCTION
Alexandrium fundyense Balech is a toxic marine dinoflagellate associated with persistent harmful algal blooms (HABs), also known as “red tides”, which cause the widespread HAB poisoning syndrome known as Paralytic Shellfish Poisoning (PSP). In North America, blooms of A. fundyense represent a newly described species comprising certain geographic groups within the “tamarense species complex”, A. catenella, A. fundyense, and A. tamarense, distinguished by the hypervariable D1-D2 region of the large subunit (LSU) rRNA gene (John et al., 2014). Blooms of this species have expanded dramatically in frequency and geographic distribution over the past few decades and recently were documented for the first time in the Arctic, including the Chukchi Sea (Gu et al., 2013, Natsuike et al., 2013) and Greenland (Baggesen et al., 2012), potentially representing a climate-driven range expansion from adjacent temperate and sub-arctic areas.
Microsatellite markers have been used to study dispersal pathways and connectivity among Alexandrium populations in Japanese coastal waters (Nagai et al., 2007), the Baltic Sea (Tahvanainen et al., 2012), and populations along the French coast (Dia et al., 2014), and have also been used to investigate the effects of sexual reproduction. In the Northwest Atlantic, microsatellite markers were used to examine the population structure of Alexandrium blooms in both coastal waters (Erdner et al., 2011) and enclosed embayments (Richlen et al., 2012). These studies utilized published microsatellite loci that were previously isolated from populations from Japan (Nagai et al., 2004) and the North Sea (Alpermann et al., 2006). However, only a subset of these loci were suitable for the analysis of A. fundyense blooms in the GOM based on amplification success and number of alleles observed (see Erdner et al., 2011), possibly due to regional differences in the genetic composition of blooms. This limitation prompted the current effort to identify new microsatellite markers from regional populations in the Northwest Atlantic. Here, we present 17 new polymorphic microsatellite loci developed for A. fundyense that can be used to investigate spatial and temporal bloom diversity, assess connectivity across geography, and investigate questions regarding dispersal events and range expansion.
MATERIALS AND METHODS
Microsatellite isolation by next-generation sequencing
Total genomic DNA was extracted from a cell pellet of an exponentially growing culture using the Power Soil kit (MoBio Laboratories Inc., Carlsbad, CA, USA). Extracted DNA was fragmented into c.a. 300–800 bps, and adaptor sequences were ligated to each end of the fragments. Resulting DNA library was subjected to shotgun sequencing on GS FLX Titanium picotiterplates using the Roche GS FLX 454 system. A total of 25,5699 sequences were obtained with total bases of 136 Mb. Assembly of these sequencing reads was performed using the Newbler Assembler software ver. 2.6 (Roche Applied Sciences, Indianapolis, IN, USA) under the default settings. Subsequent contigs and singletons were screened using a Perl pipeline coupling Tandem Repeats Finder ver. 4.0.4 (Benson 1999) and PRIMER 3 ver. 2.2.2 beta (Rozen and Skaletzky 2000), to design primers for the potential microsatellite loci (Nakamura et al. 2013; Nagai et al. 2014). A total of 2,334 pairs of primers with di-, tri-, tetra-, penta, hexa, hepta, and octa-nucleotides motif loci were designed, of which 52 primer sets were selected for initial amplification trials.
Cultured strains
A total of 31 isolates of North American A. fundyense were selected from the culture collection maintained by Dr. Donald Anderson’s lab at the Woods Hole Oceanographic Institution, and used to screen candidate microsatellite loci (Table 1). Cultures were established over the span of several years, either from single cell isolations from bloom populations (as in Erdner et al. 2011 and Richlen et al. 2012), or from germinated cysts (see Nagai et al. 2007). For the latter, cysts were isolated from sediment cores collected in the Gulf of Maine (GOM), Bay of Fundy (BOF), and the Nauset Marsh System (NMS); after germination, single vegetative cells were isolated by micropipetting and established in culture. One isolate “hybrid” was established during cyst formation experiments and represents a cross between A. fundyense strains from the NMS and BOF. Vegetative cells were isolated from blooms in the NMS and GOM. Isolates were confirmed to be A. fundyense via amplification with species-specific primers (Scholin et al., 1994, Dyhrman et al., 2006).
Table 1.
Details regarding isolates used to characterize the 17 microsatellite markers; GOM=Gulf of Maine, NMS=Nauset Marsh System.
| Isolate | Isolation location | Year | Isolation method |
|---|---|---|---|
| GT7 | Bay of Fundy | 1976 | Single vegetative cell |
| GTCA28 | GOM | 1985 | Single cell from cyst germination |
| 38-3 | GOM | 1993 | Single vegetative cell |
| CB-601 | GOM | 1997 | Single cell from cyst germination |
| 2000-CB-08 | GOM | 2000 | Single vegetative cell |
| GOM D2 | GOM | 2005 | Single vegetative cell |
| GOM F14 | GOM | 2005 | Single vegetative cell |
| GOM H15 | GOM | 2005 | Single vegetative cell |
| 17C8C | Hybrid | 1987 | Single cell from cyst germination |
| ATSP7-D9 | NMS | 2009 | Single vegetative cell |
| N5-MP3 | NMS | 2012 | Single vegetative cell |
| N6-SP3 | NMS | 2012 | Single vegetative cell |
| 28 Jan D10-E3 | NMS | 2014 | Single cell from cyst germination |
| 22 Dec D7-C5 | NMS | 2014 | Single cell from cyst germination |
| 3Feb_Am_C7 | NMS | 2014 | Single cell from cyst germination |
| 6Mar_Am_B8 | NMS | 2014 | Single cell from cyst germination |
| 6Mar_Am_D11 | NMS | 2014 | Single cell from cyst germination |
| 21May_Ch2_C2 | NMS | 2014 | Single cell from cyst germination |
| 21May_Ch2_B6 | NMS | 2014 | Single cell from cyst germination |
| 21May_Ch2_D6 | NMS | 2014 | Single cell from cyst germination |
| 21May_Ch2_D7 | NMS | 2014 | Single cell from cyst germination |
| 21May_Ch2_D9 | NMS | 2014 | Single cell from cyst germination |
| 21May_Ch2_C11 | NMS | 2014 | Single cell from cyst germination |
| 21May_Ch2_B10_2 | NMS | 2014 | Single cell from cyst germination |
| 6May_Am_C2 | NMS | 2014 | Single cell from cyst germination |
| 6May_Am_B3 | NMS | 2014 | Single cell from cyst germination |
| 6May_Am_C3 | NMS | 2014 | Single cell from cyst germination |
| 6May_Am_C7 | NMS | 2014 | Single cell from cyst germination |
| 6May_Am_B8 | NMS | 2014 | Single cell from cyst germination |
| 6May_Am_B9 | NMS | 2014 | Single cell from cyst germination |
Microsatellite genotyping and analysis
To investigate the characteristics of the 17 candidate microsatellite loci, DNA was extracted from concentrated cell pellets of each culture (~2 mL) using the Power Soil kit (MoBio) following the manufacturer’s instructions. Amplifications were performed following a nested PCR method described by Schuelke (2000). Each PCR reaction mixture (10 μl) contained approximately 5ng template DNA, 1× PCR buffer, 2.5mM MgCl2, 0.2mM dNTP, 0.5mM FAM-labeled universal M13 primer (5´– TGT AAA ACG ACG GCC AGT – 3´), 0.5mM of designed reverse primer, 0.1mM of designed forward primer, and 0.1U Ampli Taq Gold (Applied Biosystems, Foster City, CA, USA). PCR amplifications were performed in an Eppendorf Mastercycler Nexus thermal cycler (Eppendorf, Hamburg, Germany) using the following cycling conditions: 94°C (5 min), then 30 cycles at 94°C (30 s), 56°C (45 s), 72°C (45 s), followed by 8 cycles at 94°C (30 s), 53°C (45 s), and a final extension at 72°C for 10 minutes. Amplification products were screened using gel electrophoresis, then products were diluted 1:50 in nuclease-free water, dried at 60°C for one hour in the thermocycler, and analyzed using an ABI 3730×l DNA Analyzer (Eurofins MWG Operon, Huntsville, AL, USA). Allele sizes were determined using Peak Scanner software v.1.0 (Applied Biosystems) and confirmed by visualizing the trace files in Geneious Pro 6.1.2 (Biomatters, Auckland, New Zealand). Dinucleotide alleles were rounded to the nearest even number and trinucleotide alleles were rounded to the nearest whole number before performing statistical analyses. Microsatellite loci allele frequency and gene diversity were calculated using Arlequin v. 3.5.1.3 (Excoffier & Lischer, 2010).
Each culture was also analyzed using a subset of nine published microsatellite loci for A. fundyense (Nagai et al. 2004, Alpermann et al. 2006) that were previously determined to be most suitable for the analysis of blooms in the GOM region (Erdner et al., 2011, Richlen et al., 2012). These analyses were carried out as described above, using the locus-specific PCR cycling conditions in Nagai et al. (2004) and Alpermann et al. (2006).
RESULTS AND DISCUSSION
The characterizations of the 17 newly identified microsatellite loci are listed in Table 2. Loci were named in the order that primers were tested, with the addition of the expected size (ES) to the nomenclature to simplify future fragment analyses. All loci yielded bright, single bands when visualized on agarose gels. Additionally, all loci, with the exception of Afun2_ES165 and Afun6_ES269, occasionally had non-amplifying PCR products, suggesting null alleles at these loci. Isolates with non-amplifying PCR product varied by locus, however, one isolate from the NMS (Eastham, MA) yielded non-amplifying PCR product for 9 of the 17 loci. The isolate was included in the loci characterization because the remaining eight loci provided informative alleles. The 17 polymorphic loci had between two and 15 alleles per locus, with an average of 7.1. Gene diversities ranged from 0.297 to 0.952, with an average of 0.712.
Table 2.
Microsatellite primers for the 17 polymorphic loci designed for Alexandrium fundyense and select characteristics of the loci; Ta = annealing temperature.
| Locus | Primer sequence (5′– 3′) | Motif | Ta (°C) |
Number of non- amplifying samples |
Number of Alleles |
Size Range | Genetic Diversity |
|---|---|---|---|---|---|---|---|
| Afun1_ES190 | F (GGAACTTTCTTAGGGGTCGTG) R (AGCCCCAAGAACTCATACCATA) |
(CCG)9 | 60 | 1 | 7 | 188–204 | 0.717 |
| Afun2_ES165 | F (GAGAGCACAAGGAAGGAAAGAA) R (GCACAACAAGAAAGGATGAACA) |
(CA)20 | 60 | 0 | 2 | 152–154 | 0.503 |
| Afun3_ES116 | F (GCATTGATATCACCATGCAATC) R (CTTGCTTGTCGGTAGCTATGTG) |
(CA)15 | 60 | 1 | 10 | 118–138 | 0.882 |
| Afun4_ES261 | F (GCGACCATGACTGAATAATGAA) R (CGTCATGTCCATTGCATCTTAT) |
(GAT)8 | 60 | 2 | 5 | 274–281 | 0.685 |
| Afun5_ES252 | F (TCGTCCAAACTCTGACTGAAGA) R (CTCGGTGTGTTGCACTAGTCTC) |
(TCG)9 | 60 | 1 | 4 | 234–262 | 0.609 |
| Afun6_ES269 | F (CGAGGACCATGAGAAAGAAAGT) R (CCCAGGTCAATCACTACTGACA) |
(AGC)9 | 60 | 0 | 4 | 273–277 | 0.297 |
| Afun7_ES182 | F (GTGTCTGTCTTTTCCCCTCAAC) R (GGAACGGACAGATAAACTACGC) |
(TGC)9 | 60 | 3 | 7 | 198–244 | 0.825 |
| Afun8_ES136 | F (ATCGATGATTCCTCAAACGACT) R (GCGATTTTCTGTAATTTGACCC) |
(GCT)8 | 60 | 2 | 4 | 144–150 | 0.569 |
| Afun9_ES394 | F (AACACAAAACAGCATACAACGC) R (AAATTGGCACCTCTGAAGTGAT) |
(CA)13 | 60 | 3 | 7 | 394–404 | 0.778 |
| Afun10_ES203 | F (GTGTGGGATGAGAGTTGCAG) R (GTCTCCGCATGCTGTACTGATT) |
(CA)12 | 60 | 2 | 11 | 170–240 | 0.892 |
| Afun11_ES285 | F (AATTCATTCTTCCCAGCAGAAG) R (TGGTCAGGTATTTGTTGACAGC) |
(CA)13 | 60 | 3 | 5 | 288–308 | 0.630 |
| Afun12_ES207 | F (GTGTGCTATGCTATGCCTCAAG) R (GACCCGTACTAGGATAACGTCG) |
(GT)13 | 60 | 8 | 2 | 202–204 | 0.403 |
| Afun13_ES156 | F (GGCCACACACTAAAACACAAGA) R (TTTGCAATGTGCAGTATGTTGA) |
(CA)13 | 60 | 7 | 11 | 150–202 | 0.891 |
| Afun14_ES321 | F (ATCCACGTCGTAAACCTGAGTG) R (ACCGTAATTATGATGGGCGTT) |
(CA)42 | 60 | 4 | 15 | 302–344 | 0.952 |
| Afun15_ES350 | F (AACTAGACGATCGAAGCACAGC) R (ATGCTGACTTGAGCAACTGTGT) |
(CAG)9 | 60 | 1 | 7 | 351–368 | 0.832 |
| Afun16_ES282 | F (TTGTGTGGTCGGTCTCAGTATC) R (GTGTTTACTTCAAGCAGTGGGC) |
(GT)29 | 60 | 1 | 13 | 238–300 | 0.931 |
| Afun17_ES120 | F (GCATTGCTTATTAAATGGCCTC) R (CAGAAAGCAGTGGAACACAAAA) |
(AT)12 | 60 | 3 | 7 | 116–142 | 0.709 |
In comparison, previously published loci were not as well suited for the Northwest Atlantic isolates. The same characterizations were performed for these markers, which are described in Table 3. Several of the markers failed to amplify one-third or more of the strains, and one isolate did not contain enough alleles for analysis (n=30). The number of alleles ranged from 2 to 9, with an average of 5.7. Additionally, diversities ranged from 0.402 to 0.855, with an average of 0.682. These markers have previously been used to study populations in the Northwest Atlantic; however, based on our comparison, use of these markers may be limited by the varying degrees of compatibility (i.e., amplification failure) with some of the populations in this region.
Table 3.
Characterization of a subset of nine previously published microsatellite loci using 30 isolates of A. fundyense identified as most suitable for the analysis of A. fundyense populations from the northwestern Atlantic.
| Locus | Source | Number of non- amplifying samples |
Number of Alleles |
Size Range |
Genetic Diversity |
|---|---|---|---|---|---|
| ATF1 | Alpermann et al., 2006 | 2 | 9 | 152–194 | 0.735 |
| Atama 4 | Nagai et al., 2004 | 14 | 2 | 116–118 | 0.525 |
| ATD8 | Alpermann et al., 2006 | 0 | 8 | 265–278 | 0.855 |
| Atama 15 | Nagai et al., 2004 | 0 | 4 | 241–263 | 0.402 |
| Atama 16 | Nagai et al., 2004 | 8 | 5 | 150–162 | 0.788 |
| Atama 17 | Nagai et al., 2004 | 5 | 3 | 132–140 | 0.507 |
| Atama 23 | Nagai et al., 2004 | 10 | 6 | 174–196 | 0.784 |
| Atama 27 | Nagai et al., 2004 | 10 | 6 | 152–164 | 0.747 |
| Atama 39 | Nagai et al., 2004 | 12 | 8 | 120–152 | 0.791 |
The 17 polymorphic microsatellite loci offer an updated resource to study the genetic structure of A. fundyense blooms in the Northwest Atlantic and adjacent coastal embayments, and for assessments of global connectivity. Previous studies successfully used markers designed with Japanese and North Sea isolates to assess the bloom dynamics and population connectivity of A. fundyense in these regions (Erdner et al., 2011, Richlen et al., 2012); however, only a subset of the primers was suitable based on amplification success and the number of alleles observed. These new markers successfully amplified A. fundyense isolates established over the span of several years, and from several different geographic locations in the GOM region of the Northwest Atlantic, including the BOF and NMS. Our expanded library of markers provides informative loci to study external factors that contribute to bloom diversity, test range expansion hypotheses, and assess additional spatial and temporal diversity questions to better understand the population dynamics of this important HAB species.
Acknowledgments
We thank David Kulis and Alexis Fischer for isolating some of the cysts and strains used in this study. Support for this study was provided by the Woods Hole Center for Oceans and Human Health through National Science Foundation (NSF) Grant OCE-1314642, National Institute of Environmental Health Sciences (NIEHS) Grant 1-P01-ES021923-01, and the research grant of international collaboration projected in Fisheries Research Agency of Japan in 2014.
Abbreviations
- GOM
Gulf of Maine
- HAB
harmful algal bloom
- NGS
next-generation sequencing
- PSP
paralytic shellfish poisoning
Contributor Information
Taylor Sehein, Woods Hole Oceanographic Institution, Biology Department, 266 Woods Hole Road, MS#32, Woods Hole, MA 02543.
Mindy L. Richlen, Woods Hole Oceanographic Institution, Biology Department, 266 Woods Hole Road, MS#32, Woods Hole, MA 02543.
Satoshi Nagai, National Research Institute of Fisheries Science, 2-12-4 Fukuura, Kanazawa, Yokohama Kanagawa, 236-8648, Japan.
Motoshige Yasuike, National Research Institute of Fisheries Science, 2-12-4 Fukuura, Kanazawa, Yokohama Kanagawa, 236-8648, Japan.
Yoji Nakamura, National Research Institute of Fisheries Science, 2-12-4 Fukuura, Kanazawa, Yokohama Kanagawa, 236-8648, Japan.
Donald M. Anderson, Woods Hole Oceanographic Institution, Biology Department, 266 Woods Hole Road, MS#32, Woods Hole, MA 02543
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