Summer Solstice

It’s 2200h as I’m writing and the sky is still brightly lit.

Clear day. Winds 10-20 knots for most of the day.

A recreational fishing boat tied up to the jetty today to settle some engine troubles. Two different fishing boats were anchored on the edge of the south boundary of the reserve.

A boat of divers were in the reserve for about an hour this morning along the east side of the island.

2 float planes crossed overhead.

A bald eagle made his regular visit for lunch in the afternoon and captured a gull.

 

 

June 20th

Clear. Westerlies all day with speed averaging around 20 knots.

1 cruise ship passed by in the morning

1 tour boat

3 cargo ships passed through the strait throughout the day

1 helicopter passed over the reserve at 1300h

Business as usual on the reserve today:

-Another female elephant seal has arrived, bringing the current count to 5
-A California sea lion was hanging out on one of the south islands
-The pair of Caspian terns was back again today

Romanzoffia tracyi : Mist maidens–The Race Rocks Taxonomy

Romanzoffia tracyi

Scientific classification
Family: Boraginaceae (Borage)
Subfamily: Hydrophylloideae (Waterleaf)
Genus: Romanzoffia
Species: R. tracyi (Jepson)
Common name: Tracy’s mistmaiden

General: Perennial herb from well-developed, brown-woolly basal tubers; stems several, ascending, long glandular-hairy, 2-12 cm tall [1].

Continue reading

Pam Birley’s Images of Race Rocks 2004-2013

newportOn this page are links to the monthly photo diaries taken on the remote cameras at Race Rocks from 2004 to 2013  by the late Pam Birley of Leicestershire England These albums were due to her almost daily commitment for a decade.  She produced a valuable record of events with her unique screen captures from Camera 5 , Camera 1 and the underwater Camera 2.

September, 2010 October, 2010 November,2010 December 2010
May, 2010 June 2010 July 2010 August 2010
January, 2010 February, 2010 March 2010 April 2010
September 2009 October 2009 November 2009 December, 2009
May 2009 June 2009 July 2009 August 2009
January 2009 February 2009 March 2009 April 2009
December 2008 November 2008 October 2008 September 2008
August 2008 July 2008 June 2008 May 2008
January 2008 February 2008 March 2008 April 2008
January 2007 February 2007 March 2007 April 2007
May 2007 June 2007 July 2007 August 2007
September 2007 October 2007 November 2007 Dec. 2007
The full collection of previous monthly Race Rocks albums done by Pam Birley November 2004 to October 07 is now at: http://tinyurl.com/2adrsp

One of Pams first submissions to us was in this set of images of eagle predation in 2004

 

 

Bald Eagles in the Rain

 

 

 

 

Bad Hair Day for the Eagles

 

 

 

 

Pams images of  Snowy Owls were a first for Race Rocks

 

 

Feature Article on Pam Birley: From:  TheThunderbird.ca News, analysis and commentary by UBC Journalism students Former Pearson College student Marc-Fawcett-Atkinson and Annie Rueter have published the following article in  about our most consistent contributor to the website, Pam Birley of Leicester England. B.C. wildlife 

 

Live Wildlife for your Living Room
ref: Anderson, Charlie,
The Province, Vancouver, B.C. ( Sunday, Nov.21, 2004
Long Distance Monitoring, the effective Citizen Science of Pam Birley” has been has been published on page 10 of the December 2010 Issue of the Friends of Ecological Reserves log.

Pam and Dennis  Birley vist Race Rocks in 2008

 

 

This link brings up all the posts involving Pam Birley

Race Rocks Mean Monthly Sea Temperature 1921-present,

Seawater Temperature: Race Rocks
Decade Comparisons:Sea Surface Temperature at Race Rocks-
 

Year Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
1921 7.1 7.3 7.7 8.5 9.5 10.3 10.5 10.3 9.8 9.1 8.2
1922 6.4 6.1 6.6 7.5 8.3 9.5 10.5 10.3 10.2 9.3 8.4 7.1
1923 7.1 6.4 6.7 7.6 8.6 9.3 10.3 10.5 10.6 9.6 8.7 7.9
1924 7.1 7.3 7.7 7.9 9 9.8 10.5 10.3 10.2 9.2 8.8 7.3
1925 6.6 6.9 7.3 8 9.2 10.1 11.1 10.8 10.2 9.2 8.3 8.2
1926 7.8 8 8.6 9.2 10.1 10.7 11.1 10.9 10.5 9.8 9.1 8.5
1927 7.6 7.4 7.8 8 8.8 9.8 10.5 10.9 10.3 9.7 8.6 7.6
1928 6.9 7.3 7.8 8.6 9.7 10.2 10.8 10.9 10.3 9.2 8.6 7.9
1929 7.1 6.3 7.1 7.8 9 9.8 10.8 10.8 10.7 9.8 8.8 7.8
1930 6.5 6.6 7.1 8.2 9.3 10 10.6 10.8 10.6 9.4 8.6 8
1931 7.8 7.8 8.2 8.8 9.9 10.6 11.5 11.1 10.7 9.6 8.6 7.7
1932 7.1 6.8 7.3 8.2 9.3 10.4 10.8 10.9 10.7 9.6 8.9 7.7
1933 7.1 6.7 7.1 8 9.1 10.2 10.5 11.5 10.1 9.6 8.6 7.7
1934 7.8 7.9 8.3 9.2 10 10.8 10.9 11.6 10.7 9.7 9.2 8.4
1935 7.2 7.2 7.5 7.8 9.2 10.1 10.5 10.5 10.7 9.7 8.2 8.1
1936 7.9 6.7 7 7.8 9.3 10.4 11.3 11.3 10.5 10.1 8.6 7.9
1937 6.6 6.4 7.7 8.7 9.9 10.9 11.7 11.5 10.9 9.9 8.5 8.1
1938 7.4 7.2 8.1 9.4 10.6 12.3 12.7 11.9 11 9.9 8.6 7.5
1939 7.4 6.6 7.1 8.6 10.3 11.4 12.2 11.1 11.4 9.7 8.5
1940 7.9 8.2 9 10 11.4 11.6
1941 10 10.5 11.2 11 10.6 9.9 9 8.5
1942 7.9 7.9 7.8 8.5 9.6 9.8 10.5 11 10.3 9.5 8.4 7.9
1943 6.8 6.7 7.1 8.2 8.8 10 10.3 10.6 10.3 9.6 9 8.1
1944 7.7 7.5 7.3 8 9.2 10.5 11 10.9 10.5 9.6 9.2 8.1
1945 7.8 7.7 7.6 8 8.8 9.8 10.1 10.5 10 9.5 8.1 8.1
1946 7.7 7.3 7.7 8.1 9.4 10.2 10.7 10.8 10.3 9.4 8.1 7.7
1947 7.1 7 7.7 8.4 9.5 10.4 10.6 10.9 10.5 9.9 9.1 7.9
1948 7.5 6.9 7.2 7.9 9 10.2 10.8 10.7 10.4 9.5 8.2 7
1949 6.1 6.1 6.9 8.3 9.4 10.1 10.3 10.2 10.5 9.5 8.7 7.8
1950 6.2 5.8 6.6 7.7 8.7 9.4 10.1 10.4 10.3 9.3 8.5 8
1951 7.5 6.9 6.7 8.1 9.2 10.2 10.4 11.1 10.9 9.5 8.5 7.7
1952 6.9 7.1 7.6 8.2 9 9.6 10.4 10.5 10.2 9.8 8.6 7.9
1953 7.8 7.9 7.6 8.1 9.3 9.8 10.6 11 10.6 9.9 9.3 8.5
1954 7.1 7.3 7.5 7.9 8.7 9.3 9.9 10 10 9.4 9.1 8.4
1955 7.5 7.1 6.7 7.5 8.4 9.3 9.8 10.2 10 8.9 7.5 6.6
1956 6.7 6.4 6.3 7.6 8.7 9.6 10.2 10.4 10.1 9.2 8.1 7.1
1957 6.3 6.2 7.2 8.1 9.3 10 10.3 10.5 10.5 9.8 8.8 8.3
1958 8 8.3 8.6 9.3 10.3 10.7 11.5 11.5 11 9.9 8.7 8.1
1959 7.6 7.4 7.9 9.1 9.7 10.4 11.3 11 10.4 9.7 8.3 7.8
1960 7.1 7.5 7.5 8.6 9.6 10.3 11.4 10.8 10.1 9.5 8.6 7.9
1961 7.9 8.2 8.4 8.8 9.4 10.3 10.9 11.3 10.6 9.4 8.2 7.5
1962 7.2 7.3 7.3 8.4 9.3 10 10.4 10.5 10.5 10 9.3 8.7
1963 7.5 7.5 7.8 8.5 9.6 10.2 10.5 10.8 10.6 10.3 9.9 8.7
1964 8.2 7.9 7.7 8.2 8.8 9.6 10.3 10.5 10 9.4 8.3 7.4
1965 6.9 7.1 7.2 8 8.8 9.8 10 10.2 10.3 9.7 9.2 8.5
1966 7.7 7.6 7.7 8.5 9 9.1 99.9 10.7 10.1 9.5 8.7 8.6
1967 7.9 7.7 7.6 8.1 8.9 9.6 10.3 10.5 10.5 9.7 9.1 8
1968 7.3 7.3 8 8.3 8.7 9.5 10.2 10.2 10.4 9.3 8.8 7.8
1969 6.5 6.3 7.2 8.1 9.1 10.2 10.4 10.5 9.8 9.2 8.7 8.1
1970 7.5 7.7 7.9 8 8.7 9.6 10.2 10.2 10 9 8.3 7.5
1971 7 6.9 6.7 7.5 8.5 9.1 10 10.6 10.4 9.3 8.3 7.3
1972 6.4 6.2 6.9 7.6 8.8 9.5 10.5 10.6 10.2 9.1 8.4 7.3
1973 7 7.2 7.9 8.4 8.6 9.2 10.1 10.3 10 9.2 8.2 8
1974 7.2 7.2 7.3 8.1 8.5 9.7 10 10.9 10.6 9.7 8.6 8.2
1975 7.3 6.8 7.2 7.7 8.7 9.4 10.2 10.4 10.4 9.6 9.2 7.8
1976 7.2 7 7 7.8 8.7 9.3 10.1 10.1 10 9.4 8.6 8.1
1977 7.6 7.9 8 8.3 8.8 9.7 9.9 10.8 10.3 9.2 8.6 7.9
1978 7.6 7.9 8.3 8.9 9.4 10.3 10.4 10.9 10.5 9.8 8.2 7.3
1979 6.5 6.9 7.5 8.3 9.5 10 10.8 10.7 10.5 9.8 9 8.6
1980 7.7 7.6 7.9 8.6 9.5 9.5 10.6 10.9 10.5 9.9 9.2 8.6
1981 8.3 8.3 8.8 9.2 9.4 9.9 10.3 10.5 10.2 9.7 9.3 8.5
1982 7.2 7.5 8 8.8 9.9 10.7 11.4 11.8 11.4 10.3 8.8 8.3
1983 8.6 8.6 9.3 10 10.6 11.3 11.7 12.4 11.4 10.3 9.5 7.7
1984 7.5 7.8 8.4 9 9.7 10.3 11.4 11.6 10.6 9.7 8.5 6.9
1985 6.8 6.8 7.2 8.2 9.6 10.6 11.5 11.6 10.8 9.6 6.8 6.4
1986 7 6.6 8 8.4 9.4 11 10.9 11.8 10.8 9.8 8.4 7.8
1987 7.6 7.9 8.3 8.9 9.8 10.6 11.1 11.5 11.1 10 9 8.2
1988 7.4 7.5 7.5 8.6 9.6 10.4 11 11.4 10.6 9.6 8.7 7.9
1989 7 5.8 6.8 8.2 9.5 10.7 11.3 11.2 11 9.9 8.9 8.2
1990 8.1 7.7 8.2 9 9.9 10.8 11.8 12.1 12.1 10.7 9.9 8.2
1991 7.1 7.7 7.9 8.4 9.7 9.7 10.8 11 11.2 10.1 8.9 8.3
1992 7.9 8.1 9.5 9.5 10.2 10.7 11.1 11.4 11 10 9.1 7.8
1993 6.7 6.7 7.6 8.6 9.7 10.8 11 11.2 11 10.1 8.5 7.9
1994 8 7.4 8.6 9.3 10.1 10.6 11.6 11.5 11.3 10.7 9.3 8.4
1995 8.2 8.6 8.8 9.2 10.2 11.2 11.8 11.5 11.3 10.2 9.4 8.9
1996 8.2 7.8 8.4 9.2 10 10.4 11.5 11.5 10.5 9.9 8.7 7.6
1997 7.7 7.9 8.1 9 10.3 10.9 11.7 12.2 11.6 11.3 9.9 9.3
1998 8.7 9.2 9.7 9.9 10.4 11.4 11.7 12.3 12.1 10.7 9.8 9
1999 8 7.8 8.1 8.9 9.5 10.4 11.1 11.5 11.9 10.1 9 8.5
2000 7.5 7.7 8.1 9.1 10 11.1 11.3 11.7 11.4 10.3 9 8
2001 7.9 7.7 8.1 8.7 9.7 10.6 11.3 11.4 11.4 10.2 9.2 8.3
2002 8.1 7.9 7.7 8.7 9.4 10.5 11,2 11.7 11.3 10.0 9.0 8.8
2003 8.8 8.5 8.7 9.2 9.9 10.9 11.3 11.4 11.4 10.9 9.0 8.5
2004 7.8 7.9 8.3 9.1 10.4 11.0 11.8 11.9 11.2 10.6 9.4 8.6
2005 7.7 8.0 8.8 9.4 10.7 11.2 11.6 12.1 11.5 10.4 9.5 8.3
2006 8.61 8.49 8.41 8.75 10.08 10.86 11.66 12.09 11.49 10.55 9.29 8.5
2007 7.8 7.9 7.9 9.0 10.0 10.2 11.2 11.6 11.0 10.0 9.0 8.0
2008 7.46 7.33 7.68 8.06 9.36 9.77 10.84 11.30 11.16 10.14 9.39 7.87
2009 7.29 7.20 7.5 8.4 9.54 10.4 11.4 11.74 11.8 10.5 9.0 7.0
2010 8.11 8.68 9.12 8.96 9.54 10.36 11.16 11.93 11.08 10.37 8.98 8.5
2011 7.8
2012
2013
2014
2016
2017
2018
2019
2020
2021
2022
2023

 

Note, The blanks for the years 1940-41 are due to the Second World War. Apparently during that time, data was not collected by a lightkeeper.

Original data was sent by the Lightkeepers and now by the Marine Protected Area Guardian of Race Rocks to the Institute of Ocean Sciences where it is compiled and displayed at

http://www.pac.dfo-mpo.gc.ca/science/oceans/data-donnees/lighthouses-phares/index-eng.htm

Decade Average GraphDecade analysis by G. Fletcher.. NOTE probable evidence of climate change

 

Pseudocnus curatus: Black brooding sea cucumber–The Race Rocks Taxonomy

 

 

by Ryan Murphy, April, 2010 See Ryan’s underwater set on Flickr with a range of invertebrates:

In the early 1980’s while doing subtidal surveys, we discovered a major concentration of the small subtidal sea cucumber Pseudocnus curatus ( formerly Cucumaria pseudocnus) living in high density off the West side of Great Race Rocks. On April16, 2004, six divers, Ramiro, Mael, Mike, Carmen, Aven and Chris were able to do a preliminary survey of the area and have produced the results shown here.
To do the survey, they ran out a reel tape measure from shore to 75 meters in a bearing of 255 degrees magnetic from peg number 7- a permanent reference peg on the very South West corner of the Island. This took them into water that is 8 to 10 meters in depth.
We are uncertain as to why this organism concentrate here in these numbers, and this also happens at other locations such as Beecher bay 3 km to the West. This is the only area we find them in at Race Rocks.
Also included in this file are the raw data values from the divers. One may clip and paste these into an EXCEL program in order to do alternate analysis.

This species is distinguished from Cucumaria pseudocurata which lives up in the mussel beds by having 10 tentacles instead of 8. It is s found in great abundance on the surface of boulders at a depth of 10 meters 60 meters offshore of the south west tip of Great Race Rock ( peg7) Counts of up to 1000 per square meter have been estimated. It can also be found intertidally among the mussel beds on the Western side of the main island.

The following count done by students of the diving activity gives an idea of how dense this species is in one location at Race Rocks. Recently Ryan Murphy found another population of this density on the Eastside  of Great Race Rock.
The book Sea Cucumbers of British Columbia, Southeast Alaska, and Puget Sound by Phil Lambert is the best source for identification of most of the 45 species of local sea cucumbers. In it he notes that the habitat of Pseudocnus curatus “in the Juan de Fuca Strait tends to be shallow subtidal in areas where the tidal currents are strong….. They nestle together in large aggregations on open rocky surfaces …..and….. are eaten by many species of sea stars……although their body wall is toxic to some fish predators providing a strong defense mechanism.”

See also Taxing Problems by Philip Lambert – Now Curator Emeritus of Invertebrates, Royal BC Museum for a description of the difficulty in classification and the need to classify by the skin ossicles.
Google Pseudocnus curatus for a link to the page describing this species..

Pseudocnus curatus Is similar to another species, Cucumaria pseudocurata which is found more shallow in the intertidal zone at Race Rocks. Both species average 1.5 to 3cm in length. C. pseudocurata has 5 bands of tube feet in single or zig zag rows. As a rule there are 8 equal sized tentacles. P.curatus on the other hand has 10 equal sized tentacles. and tube feet scattered on the Dorsal side. At Race Rocks, it lives in the subtidal zone at 8 to 10 meters in depth.

Domain Eukarya
Kingdom Animalia
Phylum Echinodermata
Sub-Phylum Eleutherozoa
Class Holothuroidea
Subclass Dendrochirotacea
Order Dendrochirotida
Family Cucumariidae
Genus Pseudocnus
Species curatus, (Lambert,1997?)
Common Name: Black brooding sea cucumber

POPULATION DISTRIBUTION at RACE ROCKS

In the early 1980’s while doing subtidal surveys, we discovered a major concentration of the small subtidal sea cucumber Pseudocnus curatus ( formerly Cucumaria pseudocnus) living in high density off the West side of Great Race Rocks. On April16, 2004, six divers, Ramiro, Mael, Mike, Carmen, Aven and Chris were able to do a preliminary survey of the area and have produced the results shown here.
To do the survey, they ran out a reel tape measure from shore to 75 meters in a bearing of 255 degrees magnetic from peg number 7- a permanent reference peg on the very South West corner of the Island. This took them into water that is 8 to 10 meters in depth.
We are uncertain as to why this organism concentrate here in these numbers, and this also happens at other locations such as Beecher bay 3 km to the West. This is the only area we find them in at Race Rocks.
Also included in this file are the raw data values from the divers. One may clip and paste these into an EXCEL program in order to do alternate analysis.

Raw Data from 0.125 meter quadrats Ramiro and Mike and Av Carmen and Chris
meters from the shore 40
41
42 0
43
44
45
46 0
47 1
48 7
49 20
50 8
51
52 9
53
54 3
55
56
57 2
58 14
59
60
61
62 20
63
64 20
65 1
66 16 1
67 8
68 25
69 2
70 19 13
71 29
72 19
73 31
74 0

 

Other Members of the Phylum Echinodermata at Race Rocks 
taxonomyiconReturn to the Race Rocks Taxonomy
and Image File
pearsonlogo2_f2The Race Rocks taxonomy is a collaborative venture originally started with the Biology and Environmental Systems students of Lester Pearson College UWC. It now also has contributions added by Faculty, Staff, Volunteers and Observers on the remote control webcams.

Garry Fletcher

Phalacrocorax pelagicus: Review of Research on Nesting and Populations

rmpelagic1We have seen a marked decline in nesting of one of the four species of seabirds which has nested traditionally at Race Rocks, Pelagic Cormorants (Phalacrocorax pelagicus). By 2007, the nesting population had been reduced to one or two nests, and from 2008 to the last season (2009 ) there were no nests at all. This population crash has been common across the Gulf Islands., and the lower end of Vancouver Island and Strait of Juan de Fuca. According to the Canadian Wildlife Service, the population of this species is estimated to be at 9000 individuals, and the pelagicus subspecies is red-listed by BC – other subspecies are stable.

In this file, I have summarized the results of several papers on research on Cormorant populations in the southern Gulf Islands and Georgia Strait. Vermeer and Rankin, 1984, did their research when the populations were on the incline, however since the 1900s, this trend has not persisted as has been reflected in the paper by Chatwin et al. The summary of their paper and the possible reasons for decline are listed near the end of this review.

The British Columbia Coastal Waterbird Survey by Badzinski et al, 2005 indicated a possible upturn in the population trend in BC.

See images of Pelagic Cormorants on Ryan Murphy’s Flickr site

The Christmas bird count records from Race Rocks reflect some of the low population numbers at that time of year, but do show an increase in the last two years, so we hope this may signify a turn in the welfare of this species. It will be interesting to track whether or not this species returns to nesting.

Population Trends in Nesting Double-Crested and Pelagic Cormorants in Canada

  • Author(s): Kees Vermeer and Leo Rankin Source: The Murrelet, Vol. 65, No. 1 (Spring, 1984), pp. 1-9 Published by: Society for Northwestern Vertebrate Biology Stable URL: http://www.jstor.org/stable/3534203 (partial listing only)
  • ABSTRACT- Breeding populations of Double-crested (Phalacrocorax auritus) and Pelagic Cormorants (P. pelagicus) were surveyed in the Strait of Georgia, British Colum-bia, in 1983. Double-crested Cormorant numbers have increased 2.4-fold and Pelagic Cormorant numbers 1.1-fold since 1975. Double-crested Cormorant populations are presently not only increasing in British Columbia but all across Canada and in the northeastern United States. These increases are thought to be the result of decreased disturbance and persecution by man.
  • The following table is presented in partial form only:
Double-crested and Pelagic Cormorant Inventory in the Strait of Georgia in 2000

  • http://www.env.gov.bc.ca/wildlife/wsi/reports/4382_WSI_4382_RPT.PDF (see complete report)
    Authors:
    Trudy A. Chatwin, Monica H. Mather, Tanya Giesbrecht May 2001
    Abstract Since the early 1990’s Double-crested and Pelagic Cormorant have shown alarming declines in nesting populations in the Strait of Georgia. This study was initiated in 2000 to provide a complete count of nesting colonies in the Strait and compare population estimate from counts completed in various years since the mid 1950’s. A complete survey of all colonies was done in 1987. Before that, counts were done in many colonies, though not annually. We surveyed 34 Pelagic Cormorant and 17 Double-crested Cormorant historic and current colonies during the 2000 breeding season. Where possible we examined nest population trends at colonies with multiple years of data. Our analyses showed that overall counts of Pelagic Cormorants were down by half and Double-crested Cormorants had declined by two-thirds since 1987. Pelagic Cormorants showed a significant decline in total nests between 1959 and 2000; although during that period, an increase in the population at Mitlenatch Island was noted. At Double-crested Cormorant colonies, two significant increasing trends were noted. Since 1983 the population at Shoal Islands has slowly increased from zero to 104 nests in 2000. Likewise the population at Mitlenatch has also increased from zero to 70 nests. However these increases do not offset the very dramatic declines in overall population size. The most profound decreases were seen at Mandarte and Great Chain Islands where most of the Double-crested Cormorants were nesting in the late 1980’s. At Mandarte Island, 1100 nests were observed in 1983, while only to 215 were counted in 2000. We suggest that the causes of declines are possibly related to a combination of Bald Eagle disturbance, change in prey availability and human disturbance. Recommendations for management and conservation are discussed.
  • The following table is presented in partial form only:

The authors express their concern for the decline in recent years with the following summation:

  • “Based on nest counts, the nesting populations of Pelagic and Double-crested Cormorants in the Strait of Georgia have shown alarming declines in the last few years. Concern is especially warranted when one compares the complete counts that were made in 1987 and 2000. The number of nests observed has decreased by 54% for Pelagic and 70% for Double-crested Cormorants. “
The reasons for the decline were summarized in the paper as follows:

  • “The populations of both cormorant species have fluctuated considerably over the 40 years of surveys. This could be due to changes in prey availability in the Strait. Cormorants feed on Pacific Herring, Gunnells, Shiner Perch and Salmon. It has been suggested that herring schools have moved north in the Strait of Georgia (Jane Watson, Pers. Comm.), which could account for the increase in both species of cormorants at Mitlenatch. However, this does not account for the loss of the Hornby Island Colony as there is a major herring spawn in that area. As well, it is difficult to explain the increase in the Shoal Islands Double-crested Cormorant colony, by shifts in herring populations.
    Other concerns for nesting cormorants are predation by Bald Eagles (Haliaeetus leucocephalus) and disturbance from boat traffic. Eagle populations have increased on the east side of Vancouver Island (Karen Morrison, Pers. Comm.). Giesbrecht (2001) showed that Eagles were the main source of disturbance to nesting Double-crested Cormorant ’s in the Strait. She observed eagles flushing birds from their nests as well as direct predation on adults/juveniles. Recreational boating and kayaking have also increased in the Strait of Georgia. Although Giesbrecht (2001) did not observe flushing by boaters in her study, anecdotal information (Moul 2001) indicates that human disturbance either by landing at a colony or flushing birds by approaching too closely exposes chicks and eggs to predation by Northwestern Crows (Corvus caurinus), Glaucous-winged Gulls (Larus glaucescens) and Bald Eagles. “
British Columbia Coastal Waterbird Survey An Evaluation of Survey Power and Species Trends after Five Years of Monitoring March 2005http://www.bsc-eoc.org/download/BCCWS%205-YR%20Report.pdf

Authors: Shannon S. Badzinski 1, Richard J. Cannings 2, Tasha Smith 2, & Jason Komaromi 3

  • Data for two of three species of cormorants show increasing trends (Double-crested
    Cormorant, Pelagic Cormorant). Both these species have shown significant declines in numbers
    at breeding colonies on the British Columbia coast between 1980 and 2000, so the results from
    this survey may indicate a stabilizing trend but further monitoring is clearly needed. Brandt’s
    Cormorants, which occur primarily as a non breeding species, show no clear population trend
    over the past 5 years.
Also from the website of the Canadain WildlifeService, Information is presented on the decline of seabirds along the Pacific Coast of Canada. So we will continue to update our population observations of this species .Garry Fletcher, February, 2010

6 month fouling records

A week before raising the turbine in April 2007, the outer Nereocystis growth was removed by the Pearson College Divers. Since the top of the turbine is in a water depth averaging 10 metres it is shallow enough for the brown Macroalgae to take foothold and within a few weeks it would have reached the surface. This algae can atttach to a solid substrate within the top 12 metres of water at Race Rocks.

Thanks to Russell Stothers of Clean Current and the Pearson College Divers for these images.

Artificial Tidepool #13 peg #5

The rockwork done to seal the southern entrance

This artificial pool was made under permit from BC Parks by Mike Slater and Garry Fletcher in June, 1999. It is part of a long range succession study.
See also below for “AFTER the HURRICANE”

AFTER THE HURRICANE OF DECEMBER 15, 2006  (newspaper item)