3. Results

2. Methods

62 Selected Studies in Biodiversity

with a strong El Niño.

that relate to climate regimes.

interpretation.

Neoagarum [20].

visualized.

Ocean Niño Index climate events are defined here as starting in the year of the end of the first La Niña closely paired with an El Niño by ≤2 months separation, where anomalies for both El Niño and La Niña exceed 1.0 on the ONI scale for 5 months or longer (available from tinyurl.com/ENSONOAA). By that definition, the starting points of climate regime shifts from the literature get changed to earlier years in some cases; 1974 rather than 1977 and 1999 rather than 2001. Since the 1989 regime shift involved only the pairing of one La Niña after a strong El Niño, it remains starting at 1989. The regime shift of 2011 [2] is designated for the end of the first of two consecutive La Niñas paired

Using search programs for a long-term SCUBA taxonomic database (3865 dives) for Strait of Georgia seabed sites [22], 1077 taxa were screened to select 171 rare or highly abundant taxa and to present the data according to climate regime periods as defined above. The majority of taxa was more uniformly abundant through the survey period and obscured any trends visible from scanning just the 171 species. We present taxon data in tabular form so that relations of biodiversity data to Ocean Niño event-based regime shifts can be

We used these biodiversity surveys to compare the abundance of sunflower stars and green urchins in Howe Sound through time, the same survey methods used for the long-term database. Surveys were conducted on SCUBA using the roving diver technique at depths from 7 to 30 m between 1984 and 2016. The relative abundance of each species observed during a dive was estimated visually and grouped into a numerical category: none = 0; few ≤10; some ≤25; many ≤50; very many ≤100; abundant ≤1000; very abundant = thousands. To calculate annual averages, maximum values for each category were used (3000 for "very abundant"). Subsequent to SSWD and the green urchin explosion, observations of Neoagarum fimbriatum abundance and spot prawn nursery settlement have enabled interpretation of cascade effects

Geographic locations of dives within the Strait of Georgia (Figure 1) shifted through the years and research priorities may have influenced the abundance averages for some years. Many of the species, however, were not the focus of special dive searches and were listed in dive summary taxon records as a matter of routine, so that most abundance records can be taken as derived by standard methods. In recent years, focus on location and abundance of Neoagarum versus green sea urchins Strongylocentrotus droebachiensis in Howe Sound has required careful

Spot prawn abundance was quantified by monitoring spot prawn nursery settlement [20]. Using settlement records, each site was scored as urchin barren or not, based on whether Neoagarum was present. At sites lacking records of urchins or Neoagarum, juvenile prawn counts greater than zero were assumed not to be an urchin barren. However, zero counts for prawns did not indicate an urchin barren, as zero counts frequently occur in dense Most of the 1077 taxa were present during all climate regimes in the Strait of Georgia, documented in 3865 dives. When aligned with climate regime event-years, 171 selected rare and abundant species showed correspondence to the Ocean Niño events (Table 1). Only rare taxa were undetected during entire regimes. For the most abundant taxa, patterns of increased or decreased abundance correspond to the years defining climate regimes, suggesting the possibility that causal relations may one day be determined. Abundance data for the 171 selected species are in Table 1 for the entire Strait of Georgia region, including Howe Sound. An asterisk indicates trace abundance.

Among the Orchophyta the Desmarestia (acidic) species occur irregularly but are of note in recent years since 1999. Neogarum jumped in abundance during the 1999 regime, whereas a search anomaly with regard to study of widespread urchin barrens and kelp recovery resulted in anomalously high abundance estimates for this kelp during 2014–2017. Limiting a data compilation to first dives at each site yielded different results, with Neoagarum absent (urchin barrens) at over half of all sites for 2014–2017. Among the Rhodophyta there were seven genera (Porphyra, Hildenbrandia, Clathromorphum, Callophyllis, Mazzella, Constantina and Opuntiella) that peaked during the 1999 regime. Note that seaweed dive identification had not advanced prior to the 1989 regime.

Among the Porifera, Leucosolenia and Adocia were mainly abundant during the 1999 regime, whereas Pachychalina and Myxilla were abundant in both the 1989 and 1999 regimes. Plocamia was abundant mainly in the 1974 and 1989 regimes, in contrast to Cliona, for example, which occurred throughout all years.

In the Cnidaria, Cribrinopsis was highest in abundance during the 1999 regime; few have been seen in recent years. Peachia was also most abundant during the 1999 regime. Similarly, Pachycerianthus was abundant during the 1999 regime, declining during the 2011 regime; Ptilosarcus was also most abundant during the 1999 regime. Halipterus was absent during the 1989 regime, abundant during the 1999 regime, then dropped out again in 2014. Stylantheca was also steady in abundance until 2014. The jellies Cyanea, Aurelia, Aequorea and various hydromedusae were especially abundant during the 1999 regime, as was the case for ctenophores.

Rare species of nemerteans were absent in the 2011 regime, as with sipunculid worms and some annelid worms. An exception is Protula pacifica, which was least abundant during the 1989 regime. Bryozoans were either lower in abundance or absent in the 2011 regime. The same was true for Brachiopoda.

In the Mollusca many species were reduced in abundance (some absent) in the 2011 regime. An exception is the very obvious species Pododesmus machroschisma, which was higher in abundance during the 1999 regime, but still remained abundant in the 2011 regime, typical for many common species not included in this table for which abundance does not fluctuate in any pattern discernable with regime shifts. Distinction of Mopalia spp. among ten different species was not achieved until 1996, yet the abundance of these species dropped in the 1999 and 2011 regimes. The common and obvious species Ceratostoma foliatum is typical of these


Year

No. dives per year

Cnidaria

Metridium farcimen

Cribrinopsis

Peachia

. . . . . . . . . . . . . . . . . . \* \* 24 \* \* . 1 4 \* \* . . . . . .

quinquecapitata

Pachycerianthus

fimbriatus

Balanophyllia

Caryophyllia

131\*

 1\*

Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades

alaskensis

Ptilosarcus gurneyi Halipteris willemoesi . . . . \*. . . . . . . . . . \* \* \* \* \* 8 1 \* 1 \* . \* \* 40 \* . . . .

Aglaophenia spp. Garveia annulata

Lafoea dumosa

Cyanea capillata

Aurelia labiata Aequorea spp. Polyorchis penicillatus . \* . . \*. . . . . . . . \* \* \* . . \* . . \* \* \* . 1 \* . . . . . . .

Clytia gregaria Eutonina indicans

Sarsia spp.

Nanomia bijuga

. \* 182 91 \* . 1 \* 18 14 37 12 \* \* 1 30 22 34 21 23 1 1 \* 1 3 4 . \* 1 . 1 \* \* \*

. . . . .. . . . . . . \* \* \* 11 \* 43 46 8 1 8 5 1 3 2 1 1 . 19 1 . \* .

. \* 1 . . . .

. \* 1 . . . \* . \* \* \* \* \* 1 1 1 \* 1 1 23 \* 1 \* 2 \* 9 1 1 1 \* \* . \* 1

.....

\*\*\*\*

111\*

 \* \* 1.

 \* \*.

 .

......

65

252124

http://dx.doi.org/10.5772/intechopen.71599

 \* 57 18 \* . 19 1 . \* 12 10 2 8 8 10 28 22 \* 1 1 \* \* 6 1 9 3 \* . 1 \* . . \* .

. 1 20 . \* . 1 18 54 6 27 11 2 \* 1 1 53 \* \* \* \* 1 \* . 9 66 \* 1 \* \* . . 1 .

. . . . .1 \* \* . \* . . 1 \* . 2 5 2 2 24 3 3 3 29 18 11 5 3 \* 1 . 1 . 2 \* \* 1 \* .. \* \* \* \* \* \* \* \* \* 1 1 \* \* 2 2 \* 1 1 1 9 \* \* \* 2 \* \* \* \*

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

#### Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades http://dx.doi.org/10.5772/intechopen.71599


Year

No. dives per year

Ochrophyta

Desmarestia spp.

Neoagarum

fimbriatum

Rhodophyta

Porphyra spp. Hildenbrandia spp.

Callophyllis spp. Mazzaella splendens . . . . . . . . . \* . \* \* 1 \* 3 1 23 1

Constantinea

Opuntiella californica . . 1 . . . . . . 9 . \* 1 \* \* 11 3 13 3

Porifera

Leucosolenia

Craniella villosa Cliona californiana

Hamaxinella

. \* \* . . . . . \* 10 1 \* \* \* \* 1 2 13 2

amphispicula

Pachychalina spp.

Adocia sp. Plocamia karykina Myxilla incrustans

. . . . . 1 21 18 57 40 19 14 11 1 10 11 84 33 46 15 . 22 . \* \* . . . . . . . . .

 . . 1 . . . . . . . . . 8 \* . 19 2 2 2 2 1 8 6 1 3 4 . 1 10 1 . \* \* .

. . 15 18 . 1 53 51 3 11 11 11 8 1 \* \* \* \* \* \* \* . . . . . . . \*.

 eleanor . \* 1 . . . . . . . . . . . . \* 1 1 \* 15 \* \* \*

 simplex . . . . . . . . . . . \* . \* \* \* 2 2 1 9 10 1 1

. . . . . . . . . . . . \* . 1 31 24 29 20 10 3 4 11 19 27 13 5 4 2 1 1 1 11 1

1122253.

 11\*

121\*

2311143111\*

122.

2341111111\*

 1\*.

 . . . .

14331\*

 \* \* \* 11

 2

.......

 1\*

 1\*

 11\*

 \*

 \*.

 .

 \* 11.

. . . . . . . . . . . . \* . . 1 22 23 20 9 1 1 1 21 6 11 30 3 1 \* \* 1 1 \*

 . . 15 . . . . . . \* . 30 50 . 1 21 35 13 11 8 8 \* 1 3 37 19 23 18 2 \* 4 \* 3 47

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

2017

64 Selected Studies in Biodiversity


Year

No. dives per year

Disporella separata

Eurystomella

Bowerbankia sp.

Diaperoforma

californica

Brachiopoda

Laqueus

vancouverensis

Terebratulina

. . \* . . . 52 . . 2 . 60 \* \* . 1 15 3 10 1 10 8 6 1 16 \* 1 2 \* \* . 6 \* .

unguicula

Mollusca

Tonicella lineata Mopalia lignosa Mopalia hindsii

Mopalia spectabilis

Mopalia sp. Lepidozona mertensii . . . . .. \* .

Lepidozona trifida

Dendrochiton

Chlamys sp. Pododesmus

macrochisma

Kellia Saxidomus gigantea

. . . . . . . . . . . . . . . . 1 1 . \* 16 \* 1 1 6 9 12 3

suborbicularis . . . . .. . . . 1 1 . \* \* . \* \* . \* \*

\*\*\*\*\*.

 \*.

......

211\*

 11 67

 flectens . . . . .. . . . . . . . . . . . \* \* \* \* . \* . . . . . . . . . . .

. . . . .. . . . . . \* 1 \* \* 1

 . 3 22 20 . 2 2 18 20 15 8 12 1 1 \* 1 1 1 1 1 \* 1 \* \* \* . \* \* . \* \* \* \* \*

. . . . .. . . . . . . . \* 1 1

. . . . .. . . . . . . . . . \* 1 1 \* \* \* 1 \* \* \* 2 2 1 \* \* 1 1 3 2

. . . . .. . . . \* \* . . \* \* \*

121\*

211\*

 11\* 2343111335122933545211\*

122111232\*

 21

 \* \* 1\*

 \* \*.

 \*.

 \* \*

 222 \*\*\*\*\*2

http://dx.doi.org/10.5772/intechopen.71599

\*\*\*\*

312\*

 \*.

 \* \* 11

Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades

 . . . . . . . . . . . . 8 . . . . . 9 1 . . \* . . \* . . . . . . . .

 bilabiata . . . . . . . . . . . . . . . . . \* . \* . . 1 21 6 . . . . . . . . .

. . . . .. . 1 \* 1 1 \* 1 . \* 1 1 \* \* 1 1 2 \* \* 1 2 . . \* . . . . .

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

#### Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades http://dx.doi.org/10.5772/intechopen.71599


Year

No. dives per year

Ctenophora

Pleurobrachia

Bolinopsis

infundibulum

Nemertea

Quasitetrastemma

. . . . .. . . . . . \* . . . \* \* \* . . 1 . \* . . . \* . . . . . . .

nigrifrons

Cerebratulus

. . . \* .\* \* . . \* . . \* . . . 1 \* . \* . . . . . . . . . . . . . .

californiensis

Sipuncula

Golfingia vulgaris

Annelida

Amblyosyllis sp.

Tomopteris

. . . . .. . . . . . . . . . \* \* \* 9 \* \* . \* . . . . . . . . . . .

septentrionalis

Ophiodromus

. . . . .. . . . . . . . . . . 1 . . . . . \* \* . . \* . . . . . . .

pugettensis

Harmothoe extenuata . . . . .. . . . . . . . . . . . \* . \* . . . \* . . . . . . . . . .

Apomatus spp. Protula pacifica Pectinaria granulata . . . . .. . . . . . . . . . \* \* \* . \* . \* . . . . . . . . . . . .

Sabellaria

. \* 1 . . . \* 1 \* 9 1 \* . . \* \* . . 18 . . . . 1 . . . . . . . . . .

cementarium

Bryozoa

Lichenopora spp.

 . . . . . . . . . . . . . . . \* 12 12 9 8 9 \* \* \* \* . 1 1 \* 2 \* 1 1 .

 . 5 2 . . . \* \*

13211122131\*

 11\*

 \* \* \* \* \* 1\*

 1\*

 \* \*

 . . . . . . . . . . . . . . . . . 1 \* \* . . . . . \* . . . . . . . .

. . . . .\* . \* \* . . .

\*\*\*\*\*\*\*\*\*\*.

 \*\*.

 . .

......

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

2017

66 Selected Studies in Biodiversity


Year No. dives per year Humilaria kennerleyi . \* \* .

Acmaea mitra Cryptobranchia

. . . .

concentrica

Crepidula adunca

Crepidula nummaria . . . .

Crepipatella

Ceratostoma

Ocinebrina lurida

Alia carinata Epitonium indianorum . \* \* \*

Calliostoma

Calliostoma

annulatum

Calliostoma

. . . .

variegatum

Calliostoma

. . . .

canaliculatum

Margarites pupillus

Trichotropsis

cancellata

Rictaxis

. \* . .

punctocaelatus

Aglaja diomedea

Aglaja ocelligera

Year

No. dives per year

Phyllaplysia

Berthella californica

Cadlina

luteomarginata

Rostanga pulchra

Triopha catalinae

Dirona albolineata

Dirona pellucida

Janolus fuscus Janolus gelidus

Hermissenda

crassicornis

Flabellina verrucosa

Arthropoda

Heptacarpus

Heptacarpus

Heptacarpus

. . . . .. . . . . . . \* \* . \* 1 1 \* . . \* \* \* \* . . \* \* . . \* . .

tenuissimus

Heptacarpus

Hippolyte clarki

Pandalus danae Pandalus stenolepis

Lopholithodes

Cryptolithodes

 typicus 1 \* \* \* \*\* \* \* \* \* \* \* \* 1 \* 1 1 \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \*

 mandtii . \* \* \* \*\* \* \* \* \* \* \* \* \* \* \* \* \* 1 \* \* \* \* \*

. . \* . 19 . . 51 . 2 1 \* . . . \* \* \* . . . 7 \* . . \* . . . . . . . .

 sitchensis . . . . .. . . . \* \* \*

\*\*\*.

..................

http://dx.doi.org/10.5772/intechopen.71599

111\* \* \* \* \* 1\* 69

 tridens . . . . . . . . . . . \* . \* 1 10 1 1 \* \* \* \* \*

111\*

 \* \* 7\*

 \* 11

 kincaidi . 1 4 . .\* \* . . \* \* \* \* \* 1 1 2 2 1 1 2 1 1 \* 1 1 1 \* \* 1 . \* 1 .

. . \* . . . 1 34 . 13 29 12 \* 9 \* 2 32 11 \* 1 \* \* \* \* 17 6 2 . \* 1 . \* \* \*

. . \* . .. . . \* \* . \* \* \* 1 \* \* \* \* \* \* \* \* 3

. 14 31 \* . \* 52 1 2 1 1 \* \* \* \*

. . . . .. . . . . . \* . . . .

. 1 2 \* \*\* 1 1 \* 2 \* 2 1 \* 1 \* 2 1 \* \* \* \* \* \* \* \* \* . \* \* \* \* \* \*

. \* \* \* .. . 1 . \* \* \* \* \* \* . \* . \* \* . . . . \*.

 . . . . . . . .

112\*

111\*

\*\*\*\*\*.

 . . . . \*.

 . \*.

 . . .

Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades

11\*.

 \* \* \* \* \* 1\*

\*\*\*\*\*.

 \*.

 \* \*

 taylori

. 57 15 \* . . . . . . 1 . . 1 . . 11 . . . . . 1 \* . 24 . . . . . . . .

. 1 1 . . . . \* . \* \* 3 1 \* \* \* \* 12 1 1 \* \* \* \* \* . \* \* . \* \* \* \* \*

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

2017

. . . . .. . . .

. 1 1 . \*. . . . 2 \* \* 8 9 \* . \* \* . \* . . . . . . . \* . \* . . . .

 . . . . . . . . . . . . . . . . . . . . . .

 ligatum

\* . 2 \*

 foliatum . 18 7 1

 dorsata

. . . .

. \* \* .

1984

1985

1986

#### Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades http://dx.doi.org/10.5772/intechopen.71599


Year

No. dives per year Humilaria kennerleyi . \* \* . .\* \* . \* \* \* \* \* . \* \* \* \* . \* . \* 1 3

Acmaea mitra Cryptobranchia

. . . . . . . . . . . . . . . . 1 1 \* \* \* \* 2 12 6 \* \* \* \* \* \* \* 11

concentrica

Crepidula adunca

Crepidula nummaria . . . . .. . . . . \* . . . . 1 \* . \* \* \* . . . . \* \* . . . . . . .

Crepipatella

Ceratostoma

Ocinebrina lurida

Alia carinata Epitonium indianorum . \* \* \* .. . . \* \* \* . \* . \* \* \* \* \* \* . . \* \* \* \* \* .

Calliostoma

Calliostoma

annulatum

Calliostoma

. . . . .. . . . \* . \* . \* \* \* \* 1 1 \*

variegatum

Calliostoma

. . . . .. . . . . . .

\*\*\*.

canaliculatum

Margarites pupillus

Trichotropsis

cancellata

Rictaxis

. \* . . .. . . . 9 1 \* \* \* \* .

punctocaelatus

Aglaja diomedea

Aglaja ocelligera

. . . . .. . . . \* \* \* . . . . . . . . . . . . . . . . . . . . . .

. 1 1 . \*. . . . 2 \* \* 8 9 \* . \* \* . \* . . . . . . . \* . \* . . . .

1 15 34 . . . 52 34 72 2 1 21 1 9 1 \* 12 \* . 1 1 \* \* \* 1 \* 10 \* . . . 1.

 ligatum

\* . 2 \* .\* \* \* . 1 \* \* \* \* \* . . \* \* \* . \* . . \* \* \* .

......

......

\*\*\*\*\*.

 . \*. ..................

 \*

 11\*

..................

 \*.

 \*\*.

. 14 1 18 . . 17 . . 1 17 11 9 . \* \* \* . \* . . . . . . . . . . . . . . 1

 dorsata

. . . . .. . . . . . . . . . . . 1 . \* \* \* . . . . . . . . . . . .

. \* \* . . . \* 17 . 1 2 1 \* 8 \* 9 \* \* . \* \* 1 . \* \* \* . . . . . . . .

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2211

\*\*\*.

 \*\*

68 Selected Studies in Biodiversity

2010

2011

2012

2013

2014

2015

2016

2017


Year

No. dives per year

Strongylocentrotus

droebachiensis

Apostichopus

californicus

Cucumaria miniata

Eupentacta

quinquesemita

Psolus chitonoides

Urochordata

Corella willmeriana

Ascidia paratropa

Cnemidocarpa

finmarkiensis

Halocynthia

aurantium

Halocynthia

Pyura haustor

Styela gibbsii Boltenia villosa Metandrocarpa

Pycnoclavella

Cystodytes lobatus

Didemnum

. 58 62 73 . 20 . \* \* 11 2 2 \* . 1 \* \* \* \* \* \* 1 \* . . . .

\*\*\*.

 . . .

71

http://dx.doi.org/10.5772/intechopen.71599

carnulentum

 igaboja

\*\*\*\*

111\*

\*\*\*\*\*\*\*\*\*\*\*\*\*.

Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

#### Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades http://dx.doi.org/10.5772/intechopen.71599


Year

No. dives per year

Elassochirus

. . \* . .. 1 . 1 1 1 \* \* \* 1 1 \* 1 \* 1 1 \* 1 \* 1 2 1 2 \* 1 \* \* 1 \*

tenuimanus

Pagurus armatus

Balanus glandula

Balanus nubilus

Semibalanus

 cariosus . \* 30 18 58 . . 17 23 1 1 10 8 \* . 9 10 22 . . . . . . . . . . . . . . . .

Echinodermata

Pisaster ochraceus

Dermasterias

imbricata

Mediaster aequalis

Pteraster tesselatus

Henricia spp.

Pycnopodia

helianthoides

Solaster dawsoni Solaster stimpsoni Ophiura luetkenii

Florometra

serratissima

Mesocentrotus

franciscanus

. 1 3 1 .. 1 . . 1 1 1 3 2 9 1 2 2 1 1 \* \* \* \* \* 1\*

 \* \*.

 . \* \* \*

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

2017

70 Selected Studies in Biodiversity


Year

No. dives per year

Jordania zonope Radulinus taylori Chitonotus pugetensis 3 43 \* 1 . . \* . . 1 2 2 1 10 \* \* 1 1 \* \* \* \* \* 1\*

Scorpaenichthys

\* \* \* \* \*\* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* . \* \* \* \*

marmoratus

Hemilepidotus

. \* \* \* \*\* \* \* \* 1 1 1 \* 1 \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* .

hemilepidotus

Anoplagonus

Podothecus

. . \* \* \*. . . . \* . \* \* \* \* . . . \* . . . . . . . . . . \* . . . .

accipenserinus

An asterisk indicates trace abundance.

A period indicates zero abundance.

Table 1.

Average abundance

 data for 171 selected seabed species in the Strait of Georgia. Shading indicates climate regimes.

Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades

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73

 inermis . . \* . \*. . . . \* . \* \* . . . . . . . . . . . . . . . . . . . . .

\* 1 \* . .\* \* \* \* 1 \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* \* . \* \* \* \* \*

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

 11\*

 \*.

 \*.

 \* \*

2010

2011

2012

2013

2014

2015

2016


Year

No. dives per year

Didemnum/

. . . . . . . . . . . \* 25 . . 10 12 1 9 15 8 1 8 53 22 38 25 5 1 1 \* \* 2 1

Trididemnum

complex

Trididemnum

Botryllus schlosseri

Botrylloides

Chordata

Clupea pallasii Engraulis mordax

Damalichthys

Embiotoca lateralis

Cymatogaster

aggregata

Sebastes caurinus

Sebastes maliger Sebastes auriculatus . \* . . . . . \* \* \* \* \* \* . . \* \* \* \* . \* \* 3 28 4 12 5 3 10 1 3 \* 2 \*

Sebastes flavidus Sebastes emphaeus Sebastes ruberrimus

Hexagrammos

decagrammus

Hexagrammos

Ophiodon elongatus

Oxylebius pictus

 stelleri . \* \* 1 \*1 1 \* \* 1 1 1 \* \* \* \* 1 2 \* \* \* \* 3 \* 1 1 \* \*

\* \* \* \* \*\* \* . \* \* \* \* \* \* \* 1 \* 2 \* 1

1111111\*

 \* \*.

 \* \* \*

112\*

 \* \*

\* \* 1 . .\* . \* 1 . 1 \* \* . . . . 1 1 1 \* \* 1 \* 1 2 2 1 \* \* . \* 9 \*

 vacca

. . . . . . . . . . \* . \* . . \* . . . . . . \* . . . . . . . . 73 92 101

. 85 149 36 . \* . . \* \* \* \* \* \* \* \* \* \* \* 22 \* 8 17 1 1 \* \* 50 2 1 . 38 1 43

 violaceus . . . . . . . . . . . . 2 1 44 1 2 24 1 8 8 8 \* 1 1 1 . . . . \* 1 \* .

. . . . .. . . . . . \* \* . . . 1 2 9 8 \* . . 13 \* \* 1 \*

.....\*

 alexi

. \* 1 \* . . . 17 . 1 \* \* 1 1 1 1 \* 12 \* 8 8 . \* \* \* . \* \* \* . . . . .

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

2017

72 Selected Studies in Biodiversity

Table 1. Average abundance data for 171 selected seabed species in the Strait of Georgia. Shading indicates climate regimes. common species, but it is included in the table owing to higher abundances during the 1989 and 1999 regimes. Dendrochiton, Kellia, Crepidula spp., Crepipatella, Epitonium, Phyllaplysia and Rostanga were gone in the 2011 regime, and Calliostoma canaliculatum, Rictaxis punctocaelatus and Aglagia deometra were gone in both the 1999 and 2011 regimes. Flabellina verrucosa has gone from high abundance during the 1989 and 1999 regimes to rarity in the 2011 regime.

Among the Arthropoda, the common shrimp Pandalus danae is included in the table as an example of a continuously abundant species, in contrast to Pandalus stenolepis with fluctuation up in abundance during the 1989 and 1999 regimes, then reduced abundance during the 2011 regime. Compare this to the stable, low abundance continuously evident for large lithode crabs. The large hermit crab Pagurus beringanus was high in abundance during most years, but has become less abundant in the last few years. The less common Pagurus armatus was elevated in abundance late in the 1989 regime and early in the 1999 regime, an abundance cycle not coincident with these designations for climate regime shifts. The Balanus species tend to be very abundant, but are less so during the 2011 regime. It should be commented that the abundance trend for Semibalanus cariosus reflects a shift in geographic location of diving effort from the more wave-exposed southern (USA) reaches of the Strait of Georgia; this species is absent from Howe Sound, for example.

adult population of high biomass with a relatively high predation capacity. As a result of loss of this predator, the urchin Strongylocentrotus droebachiensis has increased to unprecedented abundance in the last several years, with resulting urchin barrens that have greatly reduced seaweed abundance. In addition to this one seastar species dying-off, other seastar species like

Figure 2. Pycnopodia helianthoides (black dashed line) and Strongylocentrotus droebachiensis (gray line) relative abundances in Howe Sound from 1980 to 2016. Bars represent two standard error. Vertical arrows indicate climate regime shifts.

1996

1998

Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades

2000

2002

2004

2006

2008

2010

2012

http://dx.doi.org/10.5772/intechopen.71599

75

2014

2016

The echinoderm population trends had cascade effects on seaweeds. An increase in urchin barrens since 2013 was evident in Howe Sound with 57% of surveyed sites recorded as urchin barrens in 2015 (Figure 3). The 3 years of 2014, 2015 and 2016 have seen very limited settlement of

1985 1988 1991 1994 1997 2000 2003 2006 2009 2012 2015

Figure 3. Proportion of juvenile prawn survey sites found to be urchin barrens, 1985–2016. Black bars indicate healthy

Pteraster and Solaster spp. are at trace abundance now.

no barren, kelp present barren, no kelp

Neoagarum kelp beds; gray bars indicate urchin barren (no kelp).

Abundance

Number of Dives

> 0

5

 10

 15

 20

 25 1980

1982

1984

1986

1988

1990

*Pycnopodia helianthoides*

*Strongylocentrotus droebachiensis*

1992

1994

Among Echinodermata, abundance of Florometra serratissima and Ophiura luetkenii increased only during the 1999 climate regime. Mesocentrotus franciscanus was high in abundance during the 1974, 1989 and 1999 regimes. Data on other echinoderms associated with cascade effects are reported below the following paragraphs on higher phyla.

Among the Urochordata, Ascidia, Pyura, Metandrocarpus and Cystodytes were high in abundance during the 1974 and 1989 regimes. These species have all become relatively rare in the 2011 climate regime. Corella and Cnemidocarpa were highest in abundance during the 1999 regime. Trididemnum and Didemnum spp. were abundant during the 1974, 1989 and 1999 regimes, but reduced in the 2011 regime. Botryllus and Botrylloides were high in abundance during the 1989 and 1999 regimes, then became rare in the 2011 regime.

In the Chordata, two southern species, the anchovy Engraulis mordax and the brown rockfish Sebastes auriculatus have become abundant in the Strait of Georgia during the 2011 climate regime. The live-bearing perches and most rockfishes are generally abundant, but Sebastes maliger and Sebastes ruberrimus became more abundant during the 1999 regime owing to observation of young fish from several successful reproductive year-classes during that decade [23]. The more rare fishes showed increases in different regimes, with Chitonotus most abundant during the 1974 and 1989 regimes and least abundant during the 2011 regime.

Among the echinoderms that were generally high in abundance until later in the 2011 climate regime, many seastars (starfish) suffered the densoviral SSWD die-off [18]. Pycnopodia helianthoides had been very high in abundance during the 1999 climate regime, declining in the 2011 regime until the seastar wasting caused a drop-out of adults in 2013 (Figure 2). The annual averages depicted in Figure 2 do not reveal the abrupt drop to nil that occurred in Sept/ Oct 2013 in various locations of Howe Sound, spreading south to north (D.M. Gibbs, personal observations). Note that only juveniles of this species occur in the area today. In contrast, the modest abundance levels in sunflower sea stars for 1980–1999 and 2006–2008 represented an

Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades http://dx.doi.org/10.5772/intechopen.71599 75

common species, but it is included in the table owing to higher abundances during the 1989 and 1999 regimes. Dendrochiton, Kellia, Crepidula spp., Crepipatella, Epitonium, Phyllaplysia and Rostanga were gone in the 2011 regime, and Calliostoma canaliculatum, Rictaxis punctocaelatus and Aglagia deometra were gone in both the 1999 and 2011 regimes. Flabellina verrucosa has gone

Among the Arthropoda, the common shrimp Pandalus danae is included in the table as an example of a continuously abundant species, in contrast to Pandalus stenolepis with fluctuation up in abundance during the 1989 and 1999 regimes, then reduced abundance during the 2011 regime. Compare this to the stable, low abundance continuously evident for large lithode crabs. The large hermit crab Pagurus beringanus was high in abundance during most years, but has become less abundant in the last few years. The less common Pagurus armatus was elevated in abundance late in the 1989 regime and early in the 1999 regime, an abundance cycle not coincident with these designations for climate regime shifts. The Balanus species tend to be very abundant, but are less so during the 2011 regime. It should be commented that the abundance trend for Semibalanus cariosus reflects a shift in geographic location of diving effort from the more wave-exposed southern (USA) reaches of the Strait of Georgia; this species is

Among Echinodermata, abundance of Florometra serratissima and Ophiura luetkenii increased only during the 1999 climate regime. Mesocentrotus franciscanus was high in abundance during the 1974, 1989 and 1999 regimes. Data on other echinoderms associated with cascade effects

Among the Urochordata, Ascidia, Pyura, Metandrocarpus and Cystodytes were high in abundance during the 1974 and 1989 regimes. These species have all become relatively rare in the 2011 climate regime. Corella and Cnemidocarpa were highest in abundance during the 1999 regime. Trididemnum and Didemnum spp. were abundant during the 1974, 1989 and 1999 regimes, but reduced in the 2011 regime. Botryllus and Botrylloides were high in abundance

In the Chordata, two southern species, the anchovy Engraulis mordax and the brown rockfish Sebastes auriculatus have become abundant in the Strait of Georgia during the 2011 climate regime. The live-bearing perches and most rockfishes are generally abundant, but Sebastes maliger and Sebastes ruberrimus became more abundant during the 1999 regime owing to observation of young fish from several successful reproductive year-classes during that decade [23]. The more rare fishes showed increases in different regimes, with Chitonotus most abun-

Among the echinoderms that were generally high in abundance until later in the 2011 climate regime, many seastars (starfish) suffered the densoviral SSWD die-off [18]. Pycnopodia helianthoides had been very high in abundance during the 1999 climate regime, declining in the 2011 regime until the seastar wasting caused a drop-out of adults in 2013 (Figure 2). The annual averages depicted in Figure 2 do not reveal the abrupt drop to nil that occurred in Sept/ Oct 2013 in various locations of Howe Sound, spreading south to north (D.M. Gibbs, personal observations). Note that only juveniles of this species occur in the area today. In contrast, the modest abundance levels in sunflower sea stars for 1980–1999 and 2006–2008 represented an

dant during the 1974 and 1989 regimes and least abundant during the 2011 regime.

from high abundance during the 1989 and 1999 regimes to rarity in the 2011 regime.

absent from Howe Sound, for example.

74 Selected Studies in Biodiversity

are reported below the following paragraphs on higher phyla.

during the 1989 and 1999 regimes, then became rare in the 2011 regime.

Figure 2. Pycnopodia helianthoides (black dashed line) and Strongylocentrotus droebachiensis (gray line) relative abundances in Howe Sound from 1980 to 2016. Bars represent two standard error. Vertical arrows indicate climate regime shifts.

adult population of high biomass with a relatively high predation capacity. As a result of loss of this predator, the urchin Strongylocentrotus droebachiensis has increased to unprecedented abundance in the last several years, with resulting urchin barrens that have greatly reduced seaweed abundance. In addition to this one seastar species dying-off, other seastar species like Pteraster and Solaster spp. are at trace abundance now.

The echinoderm population trends had cascade effects on seaweeds. An increase in urchin barrens since 2013 was evident in Howe Sound with 57% of surveyed sites recorded as urchin barrens in 2015 (Figure 3). The 3 years of 2014, 2015 and 2016 have seen very limited settlement of

Figure 3. Proportion of juvenile prawn survey sites found to be urchin barrens, 1985–2016. Black bars indicate healthy Neoagarum kelp beds; gray bars indicate urchin barren (no kelp).

to warmer sea surface temperatures in southern California following the 1972–1973 El Niño and the paired 1973–1974 La Niña. The analysis in [24], however, was based on biotic data from 1974 onwards, not considering what may have occurred during the 1972–1973 El Niño, so that it cannot be determined whether 1974 or 1977 was the actual tipping point. The winter of 1976–1977 was actually a weak El Niño following three consecutive La Niña winters. Both the mid-1970s and the turn of the millenium involved three consecutive La Niña winters, whereas 1988–1989 was a single La Niña event and 2010 was the start of two La Niña winters. The coincidence of taxon abundance increases with the end of the first rather than the third La Niña after the 1997–1998 El Niño suggested the rule adopted in this treatment of designating the start of a climate regime shift as the end of the close pairing of strong El Niño and La Niña events. Different taxon data may enable

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77

Extreme La Niña events are predicted to become more frequent under global warming [25, 26]. If biodiversity changes after climate regime shifts result from warming trends, then it would be expected that species would drop-out in the southern extremities of their geographic range [27]. Of the eleven species that could not be detected in the Strait of Georgia during the 2011 climate regime, not one of these species is characterized by being at the southern extreme of their distribution; indeed a few were at the north end of their range [28]. Thus, there is no signal of global warming in these data with respect to species drop-out. On the other hand, the increase of more southern fishes like anchovy and brown rockfish after 2011 coincides with aspects of warm sea surface waters since 2011. The very high taxon abundances notable for the 1999 climate regime occurred during a period characterized by three consecutive weak El Niños without intervening La Niñas. In contrast, the 2011 climate regime was characterized by the anomalous "warm blob" that appeared in 2013 [29], followed by the 19-month El Niño that peaked in winter 2015–2016 with 5 month maximum anomalies (ONI) averaging >2.0,

arguably the strongest such event yet recorded in terms of duration plus intensity.

This chapter uses ONI climate events rather than PDO, as mentioned. Ref. [30] examined the relation of zooplankton and salmon production with respect to climate-driven regime shifts. Particularly with respect to the Pacific Decadal Oscillation (PDO) [5], the analysis has been with regard to productivity and physical oceanography of the surface layers of the sea where salmon live; Ref. [5] found no relationship between Pacific salmon abundance and ONI indices. The present discussion, however, is of seabed biodiversity; the regime shifts defined from El Niño and La Niña pairings (Ocean Niño Index events) may be more relevant than PDO events to productivity and physical processes in deeper layers of the ocean. The seabed biodiversity trends discussed here do not coincide with Pacific Decadal Oscillation events the

One of the possible impacts of an ONI climate regime shift can be cascade effects of the biodiversity shifts tabulated here (Table 1). Cascade effects may lag the timing of climate regime shifts. The reduction in sunflower stars and increase in green urchins following the 2013 SSWD was unprecedented. The increase in urchins after Sept. 2013 exceeds any previous abundance of green urchins recorded in our 1984–2016 database. The reduction of Neoagarum beds (Figure 4) following the urchin increase could lead to a further cascade effect. Since the spot prawn is a strict protandric hermaphrodite [20], two successive years of very low nursery

analysis of biodiversity shifts after 1974 versus 1977.

way they do with Ocean Niño Index events.

Figure 4. Juvenile Pandalus platyceros abundance in kelp beds from 1985 to 2016 at four reefs in Howe Sound, British Columbia. Open circles indicate years where reefs were an urchin barren; closed circles indicate presence of kelp bed (no urchin barren).

spot prawns in Neoagarum nursery habitat, despite modestly high settlement rates in the very few small patches of remaining Neoagarum in Howe Sound (Figure 4). Anecdotally, local prawn fisheries have contracted over the last 2 years, with reports of few small, young prawns in catches.

#### 4. Discussion

As previously suggested [6], it appears that marine life provide a refined method of designating climate regime shifts. The biodiversity data presented here also suggest that the modification of regime start-years from those suggested (1977, 1989, 2001) by previous literature [1] to the uniformly defined years presented here (1974, 1989, 1999, 2011) may provide a superior basis for predictions of seabed biodiversity changes with climate regime shifts. The present data correspond more closely to 1999 as a regime start rather than 2001, as was suggested in Ref. [4], which indicted 1988–1989 and 1998–1999 as climate regime shifts. Ref. [3] had indicated that 2000–2001 was the millennial regime shift.

Our data are not adequate for analysis of 1974 versus 1977 for the start of that earlier climate regime shift. Abundant analysis of oceanographic data [5, 6, 24] show that 1977 marked the change to warmer sea surface temperatures in southern California following the 1972–1973 El Niño and the paired 1973–1974 La Niña. The analysis in [24], however, was based on biotic data from 1974 onwards, not considering what may have occurred during the 1972–1973 El Niño, so that it cannot be determined whether 1974 or 1977 was the actual tipping point. The winter of 1976–1977 was actually a weak El Niño following three consecutive La Niña winters. Both the mid-1970s and the turn of the millenium involved three consecutive La Niña winters, whereas 1988–1989 was a single La Niña event and 2010 was the start of two La Niña winters. The coincidence of taxon abundance increases with the end of the first rather than the third La Niña after the 1997–1998 El Niño suggested the rule adopted in this treatment of designating the start of a climate regime shift as the end of the close pairing of strong El Niño and La Niña events. Different taxon data may enable analysis of biodiversity shifts after 1974 versus 1977.

Extreme La Niña events are predicted to become more frequent under global warming [25, 26]. If biodiversity changes after climate regime shifts result from warming trends, then it would be expected that species would drop-out in the southern extremities of their geographic range [27]. Of the eleven species that could not be detected in the Strait of Georgia during the 2011 climate regime, not one of these species is characterized by being at the southern extreme of their distribution; indeed a few were at the north end of their range [28]. Thus, there is no signal of global warming in these data with respect to species drop-out. On the other hand, the increase of more southern fishes like anchovy and brown rockfish after 2011 coincides with aspects of warm sea surface waters since 2011. The very high taxon abundances notable for the 1999 climate regime occurred during a period characterized by three consecutive weak El Niños without intervening La Niñas. In contrast, the 2011 climate regime was characterized by the anomalous "warm blob" that appeared in 2013 [29], followed by the 19-month El Niño that peaked in winter 2015–2016 with 5 month maximum anomalies (ONI) averaging >2.0, arguably the strongest such event yet recorded in terms of duration plus intensity.

This chapter uses ONI climate events rather than PDO, as mentioned. Ref. [30] examined the relation of zooplankton and salmon production with respect to climate-driven regime shifts. Particularly with respect to the Pacific Decadal Oscillation (PDO) [5], the analysis has been with regard to productivity and physical oceanography of the surface layers of the sea where salmon live; Ref. [5] found no relationship between Pacific salmon abundance and ONI indices. The present discussion, however, is of seabed biodiversity; the regime shifts defined from El Niño and La Niña pairings (Ocean Niño Index events) may be more relevant than PDO events to productivity and physical processes in deeper layers of the ocean. The seabed biodiversity trends discussed here do not coincide with Pacific Decadal Oscillation events the way they do with Ocean Niño Index events.

spot prawns in Neoagarum nursery habitat, despite modestly high settlement rates in the very few small patches of remaining Neoagarum in Howe Sound (Figure 4). Anecdotally, local prawn fisheries have contracted over the last 2 years, with reports of few small, young prawns in catches.

Figure 4. Juvenile Pandalus platyceros abundance in kelp beds from 1985 to 2016 at four reefs in Howe Sound, British Columbia. Open circles indicate years where reefs were an urchin barren; closed circles indicate presence of kelp bed (no

Cates Bay Grace Islet

Popham Pam Rocks

1985 1995 2005 2015

1985 1995 2005 2015

As previously suggested [6], it appears that marine life provide a refined method of designating climate regime shifts. The biodiversity data presented here also suggest that the modification of regime start-years from those suggested (1977, 1989, 2001) by previous literature [1] to the uniformly defined years presented here (1974, 1989, 1999, 2011) may provide a superior basis for predictions of seabed biodiversity changes with climate regime shifts. The present data correspond more closely to 1999 as a regime start rather than 2001, as was suggested in Ref. [4], which indicted 1988–1989 and 1998–1999 as climate regime shifts. Ref. [3] had indi-

Our data are not adequate for analysis of 1974 versus 1977 for the start of that earlier climate regime shift. Abundant analysis of oceanographic data [5, 6, 24] show that 1977 marked the change

4. Discussion

urchin barren).

) E

76 Selected Studies in Biodiversity

U

P

C(

ecnadnubA

0

1985 1995 2005 2015

1985 1995 2005 2015

cated that 2000–2001 was the millennial regime shift.

One of the possible impacts of an ONI climate regime shift can be cascade effects of the biodiversity shifts tabulated here (Table 1). Cascade effects may lag the timing of climate regime shifts. The reduction in sunflower stars and increase in green urchins following the 2013 SSWD was unprecedented. The increase in urchins after Sept. 2013 exceeds any previous abundance of green urchins recorded in our 1984–2016 database. The reduction of Neoagarum beds (Figure 4) following the urchin increase could lead to a further cascade effect. Since the spot prawn is a strict protandric hermaphrodite [20], two successive years of very low nursery recruitment in absence of Neoagarum beds could result in a population in Howe Sound consisting of mostly females for the winter of 2017/2018. This would lead to expectation of very little successful fertilization of eggs, a negative feedback loop that would further exacerbate the limit to nursery settlement that results from low availability of Neoagarum kelp beds. The reduction in sunflower stars, however, started with the 2011 regime shift, then was exacerbated by the SSWD, with further cascades through urchins, kelp and prawns following.

the current level of citizen science focused on sea star wasting, many areas remain uninvestigated, so the fate of the prawn fishery in Howe Sound and Strait of Georgia waters will be an important indicator of ecosystem status from the standpoint of Neoagarum kelp beds. Ref. [16] discusses the densovirus die-off of various seastar species in the Strait of Georgia that resulted in the very high sea urchin abundance evident for the last several years. This may have driven cascade effects that reduced seaweed abundance and associated fauna. It is not clear, however, that all the biodiversity changes associated with this 2011 climate regime shift relate to the seastar collapse. It seems more likely that the anomalous "warm blob" followed by a record El Niño event may have affected overall ecosystem processes. The determination of how global warming interacts with regular Ocean Niño Index events remains a foremost

Seabed Biodiversity Shifts Identify Climate Regimes: The 2011 Climate Regime Shift and Associated Cascades

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79

Although caveats about global warming always need acknowledgment, the principal finding in this book chapter of close correspondence of biodiversity shifts to naturally occurring climate regime shifts is a positive sign. Both increases and decreases in species abundance tend to coincide with climate regime shifts that have occurred regularly as a fundamental aspect of weather and climate on earth. Examination of long-term biodiversity databases should include

Alejandro Frid assisted with manuscript review and editing. Jessica Schultz assisted with diving and manuscript preparation. Kris Moulton created the map of study regions. Portions of the diving for this work were funded by donations from members of the Howe Sound Research and Conservation Group of the Vancouver Aquarium Coastal Ocean Research Insti-

\*, Donna M. Gibbs1,2, Laura A. Borden1 and Charles J. Gibbs<sup>2</sup>

[1] Marliave JB, Gibbs CJ, Gibbs DM, Lamb AO, Young SJF. Biodiversity stability of shallow marine benthos in Strait of Georgia, British Columbia, Canada through climate regimes, overfishing and ocean acidification. In: Grillo O, Venora G, editors. Biodiversity Loss in a

concern for future observations and analysis.

comparisons to ONI climate regime cycles.

\*Address all correspondence to: jeff.marliave@ocean.org 1 Ocean Wise Coastal Ocean Research Institute, Canada

2 Pacific Marine Life Surveys Inc., Canada

Acknowledgements

tute.

Author details

Jeffrey B. Marliave1

References

The present data compilation is the first to reveal the full decade of extraordinary sunflower star abundance during the millennial climate regime of 1999–2011, as well as the drop in abundance coincident with the 2011 regime shift (Figure 2). That drop in abundance coincident with the paired La Niñas of 2010–2012 could have resulted from some loss of condition factor during the cool conditions that then were followed by the SSWD event of 2013. A SSWD event with Pisaster in Oregon correlated with cooler temperatures rather than warmer [31]. We must note that the continuing SSWD of other sea star species such as Pisaster ochraceus in 2014 has only resulted in up to 80% mortality in populations [31]. This contrasts to the reduction to nil abundance, as occurred in the present observations of Pycnopodia helianthoides in Howe Sound (Figure 2) and in 1978 with Heliaster kubinjii in the Gulf of California [10]. Further, no discussion to date of proximate (SSWD) versus ultimate factors [31] has considered climate regime shifts as a possible ultimate factor.
