A new Lease on Life for the Rare Marsh Plant: Phragmites australis subsp. americanus–A note of caution when attempting to control Invasive Species

By Garry Fletcher, Metchosin, British Columbia

goochcreekpops

The yellow dots show the margin of the Gooch Creek Estuary. The populations of native Phragmites are shown in red. Location: 48deg,22′,11.01″N—123deg 31’52.19″ W.

 

Introduced species are no doubt one of the most serious challenges for us in the effort to preserve ecological integrity*. Occasionally however we can mete out  a death sentence to an innocent which can have serious consequences.  This post is about one such occurrence with the native marsh/estuary grass Phragmites australis (Cav.) Trin. ex Steud. subsp. americanus

When we first bought our property on William Head Road, I was intrigued with the variety of ecosystems that could fit into one small 4 hectare piece of land. One such ecosystem was the  seasonally flooded salt marsh at the foot of the property. In that marsh were two populations of a very tall (2-3 metre) marsh reed grass.

In the mid-1980s, I asked one of our members of * MEASC, Robert Prescott-Allen to identify the species for me and he came up with the genus name Phragmites. He indicated that it used to be more common in our coastal estuaries, but it had been destroyed in the early years with cattle trampling and grazing. Now it only occurs in limited  populations in BC and in some populations along the Oregon Coast.

When I made the website MetchosinCoastal , I included a profile on the marsh with images of this plant on the Taylor Beach/Gooch Creek page . phragmiteskalleFast forward twenty years or so until 2009. I received a call from the Invasive Plant EDRR Coordinator | B.C. Ministry of Forests, Lands & Natural Resource Operations
PO Box 9513, 8-727 Fisgard St, Victoria B.C. CANADA V8W 9C1. She indicated that there were 9 populations of the introduced species Phragmites australis (Cav.) Trin. in BC and it was their mandate to control all of them. She came out to the farm, took samples and pictures and I sent her pictures of the extent of the grass in the marsh over the last few years indicating it really hadn’t spread that much. She made reference to a sample in the RBC museum which had been collected from our pond in 1992 which was identified as the introduced variety.

She indicated she would be out with a crew in the fall to cut the plants to the ground and spray with the herbicide Glyphosate . (and this being next to a sea-run cutthroat stream!)

On their website, the locations of this plant in BC were identified .  When the call came that they were coming out, I started to do research on the species.  I valued this plant as a great nesting habitat for red-winged blackbirds, and in the summer they get infested with aphids, providing food to wasps, marsh wrens and other birds. In addition, the hollow stems made excellent homes for Mason Bees.

2013-05-15redstem3

The red stems mentioned on the Oregon ID website are visible in the growing season on our population of reeds. I checked in early Dec.2013 and the red color is still visible.

I referred to a website from the Government of Oregon, which gave a comparison on the physical features of native , (Phragmites australis subsp.americanus) and introduced species samples. It looked very much like the native species to me, with most of the morphological characteristics corresponding. It also indicated that DNA analysis of tissue samples was the only definitive way to determine the genotype of the species.

I also contacted Dr. Adolf Ceska for his opinion, he indicated that the invasive variety probably came into BC in the 1980s. This population in our marsh was well established before the 1980s, and has not progressed very much since then. It is in a seasonal estuary, it floods with fresh
This species reproduces both asexually by underground rootstalks as well as sexually by seeds born on panicles such as this.

This species reproduces both asexually by underground root-stalks as well as sexually by seeds born on panicles such as this.

water with heavy winter rains,  but only gets flooded with a salt water intrusion at high tides driven by a east-wind driven storm surge. (winter only)

phragmitestassleoct13I tend to think that the salt water controls its distribution  somewhat in this particular marsh.  Interestingly,  in recent years cattails have spread  in the pond and they were previously also controlled by salt water. The main invasive in the marsh is reed canary grass.

I told the  Invasive Plant EDRR Coordinator when she showed up with her crew of two to “remove it”  that I would not allow it unless it was proven to be the invasive by DNA analysis.  I heard back from her in the spring 2014.
Phragmites australis subsp. americanus growing in the Gooch Creek marsh

Phragmites australis subsp. americanus growing in the Gooch Creek marsh (in November) of the year

In December of 2013, I was contacted by a wetlands restoration company from Nanaimo, BC about the population, as  they found out from the RBC museum that our population was the native variety. I had not heard this yet so I contacted Dr. Ken Marr at the museum, and he indicated that DNA tests had been done and that it was indeed the native species.

 

  • He writes “At this very moment I happen to be at UVIC looking at the raw data from the DNA analysis that was mostly completed a year ago.  We have been doing a parallel study of morphology and DNA of 140 or so samples of Phragmites.  Long story short, we have determined from the DNA analysis, that the populations on your land are the native genotype.  In fact, the analysis of the the sample from your land convinced the coordinator of the value of doing the DNA analysis since she had thought the plants on your land were the invasive genotype. Her conclusion may have been based upon my tentative ID of a specimen collected in 1992(?) from your land and that I thought to be the invasive genotype using the characters that have been used to distinguish the native from the invasive. All who have worked on this group acknowledge that for some individual plants, it is difficult to be certain which genotype to which a plant belongs, however DNA markers are viewed to be unambiguous.”
So having regained its “native species” reputation it is protected. The moral of the story is that we must not act impulsively on eliminating introduced species unless we are absolutely certain of the species, and in the case of Phragmites, DNA testing is a minimum requirement before extirpation is promoted.
This has ben published in the BEN ( Botanical Electronic Newsletter)  http://bomi.ou.edu/ben/ben475.html
  • One value added  aspect of the dead hollow stems of Phragmites australis subsp. americanus is that they make great Mason Bee homes. The bottom metre and a half of the larger stems have internode lengths of up to 20 cm, and the inside diameter of the stems is 8 mm.

REFERENCES:

1.BEN , Botanical Electronic News: References on the identification of native and introduced varieties of Phragmites
2. Native to North America or introduced (or both)?
Information on the Morphological Differences between the Native and Introduced
3. Saltonstall, K., Burdick, D., Miller, S., and Smith B. 2005.  Native and Non-native Phragmites : Challenges in Identification, Research, and Management of the Common Reed,  National Estuarine Research Reserve Technical Report Series 2005. (This publication has a good set of comparative photographs of the two varieties.)
4. Swearingen, J. and K. Saltonstall. 2010. Phragmites Field Guide Distinguishing Native and Exotic Forms of Common Reed (Phragmites australis) in the United States. Plant Conservation Alliance, Weeds Gone Wild.
5. from The Encyclopedia of Earth,   Phragmites australis – cryptic invasion of the Common Reed in North America, “Kristin Saltonstall of the Smithsonian Tropical Research Institute has conducted a series of groundbreaking genetic analyses on P. australis. Her research has identified 29 unique genetic types, or haplotypes, of the grass globally. Of these, 13 are native to North America and historical pre-1910 samples indicate a wide distribution of these native haplotypes across the continent. Modern sampling has revealed the widespread presence of a non-native haplotype growing throughout North America. This newcomer’s DNA matches that of a Eurasian haplotype that is the most common P. australis haplotype in the world.”

Kingdom Plantae – plantes, Planta, Vegetal, plants
Subkingdom Viridaeplantae – green plants
Infrakingdom Streptophyta – land plants
Division Tracheophyta – vascular plants, tracheophytes
Subdivision Spermatophytina – spermatophytes, seed plants, phanérogames
Infradivision Angiospermae – flowering plants, angiosperms, plantas com flor, angiosperma, plantes à fleurs, angiospermes, plantes à fruits
Class Magnoliopsida
Superorder Lilianae – monocots, monocotyledons, monocotylédones
Order Poales
Family Poaceae – grasses, graminées
Genus Phragmites Adans. – reed
Ed. Note: Species subspecies americanus is the native species
in North America. Phragmites australis (Cav.) Trin. ex Steud. – common reed
-introduced species in North America

See posts on the use of Phragmites stems for culturing Mason Bees here:http://www.gfletcher.ca/?tag=phragmites

 

BC Government Publications Index for Stewardship Centre on Coastal Planning and Land Use

BC Government Publications
Index for:
Stewardship Centre for British Columbia
Coastal Shore Stewardship: A Guide for Planners, Builders and Developers on Canada’s Pacific Coast

http://www.llbc.leg.bc.ca/public/pubdocs/bcdocs/368207/

The four PDFs linked to this government site have also been included here since we find that external URLs often change:
Part 1: Coastal Shore Stewardship A Guide for planners, Builders and Developers on Canada’s Pacific Coast: part1

Part 2  Coastal Planning and Approvals, Who does What: part2

Part 3  Don’t disrupt, Don’t harden, Don’t pollute: Land Development,  Marine Facilities, Seawalls and Revetments, etc.   Links to many  Stewardship resources; part3

Internet resources: internetaddresses

Anthropogenic habitat modification from Witty’s lagoon to the south side of Albert Head.

This area has in the past been modified significantly from the natural shoreline. Several seawalls have been installed in the past to deal with drainage problems or erosion threats , or to improve sea views or add to usable property on the foreshore. Typically land owners do not like to be criticized for actions on their properties which they believe will be constructive. However current  standards as outlined  in the documents “BC Government Publications Index for Stewardship Centre on Coastal Planning and Land Use” would probably not allow such impacts any more.

 

The images below were from earlier aerial photos of other modifications in the area.

Aerial views courtesy of the CRD NATURAL AREAS ATLAS

Return to the sector 8 

Some interesting statistics about the shoreline of Metchosin

If one goes to the CRD Natural Areas Atlas and uses the measurement tools, you can find out some interesting facts about the extent of Metchosin’s Coastline.

The total land based shoreline of Metchosin : 48,660 metres (48.6 km)

Total length of shoreline around islands off Metchosin’s shore:
23,118.5 metres (23 km)

Total length of the shoreline of the Race Rocks Islands: 3500 metres.  (3.5 km)

 

Sharing our Shoreline

Values and Views
Island Trust Communities
Marine By Nature
The Islands within the Salish Sea have been  shaped by ancient glaciers and modern oceanic forces. Whether you visit the islands seasonally or live here year round, Islanders treasure the marine environment.  The North Pender Local Trust Committee has developed this brochure to introduce you to where sensitive marine habitats exist, how you can recognize them, and what simple steps you can take to ensure our local waters continue to support a vibrant and abundant marine ecosystem.

This PDF has been produced by the North Pender Island Local Trust Committee: Sharing Our shorelines_lowres

IslandstrustContents:

Clean Water
Shoreline erosion
Coastal Bluffs and Shoreline beaches
Marine Riparian Vegetation
Intertidal Habitats
Beach-spawning Forage Fish
Eelgrass habitats
Kelp Forests and Rocky Reefs
Marine shorelines as critical fish habitats

Eel grass Distribution along Parry Bay

Eel grass along our coastline provides a valuable habitat for juvenile fish, crabs and other invertebrates. This week on October 28 and 29th, there was a wind from the North West which resulted in some debris deposition on the beach. The pictures show the eel grass deposits and the map shows the location where it came from  in the shallow water offshore. Eel grass turned up in the strand line almost the full length of the Taylor beach sector:

It is also important to note that the rocks along the beach at 0.5 M tide level just to the north of Taylor road are covered in Surf grassPhylospadix sp.

eelgrassnov1b

View from the south end of Taylor Beach showing Eel grass in the strand line

eelgrassnov1

View from the North end of Taylor Beach showing Eel grass in the strand line

eelgrassbed

Metchosin’s Protected Trees

METCHOSIN’S PROTECTED TREES

You can download this in a PDF:TREE BROCHURE print

ANY NATIVE TREE ONE METRE DBH AND ABOVE

DBH = diameter at breast height (1.3m)

Almost any native tree that is measured at one metre dbh will be at least 150 years of age. Large, old trees supply critical habitat for woodpeckers, bears, and many other species, and older trees have a crucial relationship with fungal root systems (mycorrhizae) that are critical to supporting forest health.

GARRY OAK

Poster child for our endangered Garry oak ecosystems and British Columbia’s only native oak tree, its calcium rich bark hosts abun- dant moss, lichen and insect communities.

PACIFIC DOGWOOD

BC’s provincial flower, its late spring floral display is breath-taking. The bright red clusters of berries are eaten by numerous birds including the blue-listed, band-tailed pigeon.

ARBUTUS

The only native, broadleaf evergreen tree in Canada, its white flowers are used by many pollinators and hummingbirds. Steller’s jays and others flock to its red or orange berries. ANY Arbutus tree 50 cm and above receives increased protection.

MANZANITA

This attractive bonsai-like shrub with red, peeling bark and ever- green leaves provides food for many bees, butterflies, humming- birds and other animals.

CASCARA

Over-harvested as a natural laxative, only the occasional young tree can still be found. Leaves turn a beautiful clear yellow in fall. Grouse and songbirds harvest the berries.

WESTERN YEW

Slow growing, it is the original source of taxol, a cancer-fighting drug. Many birds eat the bright red fruit (poisonous to humans) and the leaves supply food for black-tailed deer.

SEASIDE JUNIPER

Very rare, tree-sized juniper that has recently been recognised as a new species; appearance is similar to Rocky Mt. juniper.

TREMBLING ASPEN

Uncommon on Vancouver Island, although common in the BC Interior, there is a healthy population that shows a beautiful, yellow, fall colour at Witty’s Lagoon.

OREGON ASH

A red-listed, species-at-risk typically found in poorly drained, humus rich soil, in swamps, estuaries and seasonally flooded habitats.

Please contact Metchosin District staff with any questions on the amended Tree Management Bylaw. 250-474-3167 or email www.metchosin.ca

Forage Fish in Metchosin

All articles and posts on the MetchosinCoastal website under the title Forage Fish may be found here:

In 2008 and in  2013, Ramona de Graaf, a biologist with the Public Education Program at the Bamfield Marine Station gave presentations on Forage Fish on our beaches  and the need to Document their occurrence. In 2008 on the Saturday after the presentation, we rejoined for a walk and a session on the process involved in sampling for Forage Fish on Taylor Beach. Ramona is also the principal and founding marine scientist of Emerald Sea Research and Consulting.

Our thanks from the Blue-Green Spaces committee to Ramona and Wen-Ling for this informative session on the importance of monitoring and preserving forage fish habitat.

See also the post: Overhanging Vegetation, Invertebrates and Forage fish

See also Forage Fish of Metchosin and Beyond by Moralea Milne with an article by Briony Penn : The herring, the Chinook and the Orca…At the Brink.  Moralea also documents a second training session by Ramona on Taylor Beach in March of 2009. Inclued is an article she wrote for the January Issue of The Metchosin Muse.

Throughout the Strait of Georgia, fish stocks have dramatically declined. Lingcod, rockfish and some Pacific salmon species are only some of the major commercial fish species in decline. Seabird populations throughout British Columbia and Washington State are also decreasing. As well, marine species such as the southern resident killer whale, dependent on salmon runs, have been listed as endangered. Many of these species depend on bait or ?forage? fishes as prey. Spawning habitat of forage fishes is located in nearshore marine environments, an environment heavily impacted by human development.

            Documenting and protecting forage fish spawning habitats must be a priority for the Metchosin Coastline.

There is little information on the current extent and health of the spawning habitats of herring and no information on the spawning habitat of surf smelt and Pacific sand lance. Surf smelt and sand lance spawn in gravel/sand beach habitats in the upper one third of the intertidal zone (Figure 1). Current spawning habitats of surf smelt and sand lance have been documented throughout the US coasts of the Juan de Fuca Strait, San Juan Islands, and Puget Sound (Penttila 2000, 2001). In Canada, eelgrass beds are protected as critical fish habitat under Fisheries and Oceans Canada ?no-net? loss policy (Federal Fisheries Act). Protecting forage fish spawning and rearing habitats will have positive benefits by protecting a vital food source for numerous marine predators. Fisheries and Oceans Canada recognizes the need to obtain information on the habitat requirements of forage fishes in Coastal areas.

intertidalzone

 

Intertidal zone spawning locations.
WHAT ARE WE CONCERNED ABOUT WITH METCHOSIN’S BEACHES?

Diversion of sediment-bearing streams through culverts, and the backshore and intertidal placement of seawalls, outfall pipes and riprap armouring interrupt natural coastal processes (such as erosion) that supply terrestrially-borne gravel sediments to beaches crucial to spawning surf smelt and Pacific sand lance. Seawalls are physical barriers that block the seaward transport of eroding gravels from feeder bluffs. Impediment of the long-shore transport of sediments by groins, outflow pipes, piers, boat ramps and docks have all contributed to the sediment-starved state of some beach faces. In general, the placement of seawalls and riprap armouring in the backshore and in the intertidal continues the process of sediment deprivation due to the action of wave scouring. Wave scouring can result in the loss of fine sands and gravels (appropriate for spawning) and the dominance of coarser (larger) gravels and cobble beaches inappropriate for use as spawning gravels for both surf smelt and Pacific sand lance. Seawalls such as those onPreliminary Habitat Assessment for suitability of intertidally spawning forage fish species, Pacific sand lance (Ammodytes hexapterus) and surf smelt (Hypomesus pretiosus) Esquimalt Lagoon, Colwood , British Columbia and Tower Point are often placed in the backshore, supralittoral and high intertidal zones (the uppermost portion of the high tide range) which can result in the loss of spawning habitat area, a decrease in beach elevation, an increase in beach slope, interruption of the sediment-transport drift cell, and the loss of sediment retaining logs. Not only are these ?hard? approaches to storm protection negatively impacting forage fish populations, but they can fail to deliver the protection intended. Around the world and locally, there are growing incidences of seawalls and other armouring failing to protect land owners. Modern engineering approaches, or ?soft? approaches work with coastal processes to provide safety for human populations and industries as well as maintaining marine ecological functions. While this report will not address this topic in detail, several informative websites and consultants include http://www.greenshores.ca, http://www.coastalgeo.com, and http:// www.sanjuans.org.
The presence of overhanging vegetation in marine riparian zones is important for the ecological function of nearshore marine habitats (Levings and Jamieson 2001; Brennan and Culverwell 2004) including having a positive effect on surf smelt spawn survival (Penttila 2001). The loss of overhanging vegetation (due to shoreline hardening measures) in the marine riparian zone has several ecological implications not only for marine fish and invertebrates, but the loss of shade cover increases the mortality of incubating surf smelt eggs (Penttila 2001, Rice 2006). Summer beach sediment temperatures are moderated by overhanging vegetation. Surf smelt eggs are typically anchored to surface gravels but are also buried between interstitial spaces within sediments layers (Penttila 2001). Surf smelt eggs deposited in summer months likely encounter high mortalities on the surface but eggs buried deeper in spawning substrates can avoid extreme surface temperatures and drying resulting in an increased survival rate (Penttila 2001). The loss of shading, however, increases thermal stress and desiccation to incubating eggs as temperatures within the sediments rise resulting in increased mortality of even buried eggs (Penttila 2001, Rice 2006). Vegetation buffers the drying effect of winds, and where beaches have lost riparian zones, eggs can also suffer a higher mortality than ?natural? due to wind-induced desiccation effects.
In Washington State, sand lance, surf smelt and other forage fish species such as anchovy are protected due to their importance to upper trophic levels of the food chain to support commercial fisheries (such as salmon, rockfish, ling god) and for ecosystem function (as advocated in WDFW principles of ecosystem management).

In general, surf smelt and Pacific sand lance depend on healthy nearshore and beach habitat, and they are vulnerable to impacts from shoreline development. Beaches with natural erosion processes supplying appropriate sized gravels and extant riparian zones are an optimal state for spawning surf smelt and sand lance. Winter spawning stocks of surf smelt may avoid desiccation stress and may have evolved to exploit beaches lacking overhanging vegetation (D. Penttila, pers. comm. 2007). Of primary importance for spawning is the mixture of gravels with a sand base. Cobbling beaches for heavy equipment operation, bulkheads, seawalls, outflow pipes and structures impeding sediment-transport drift cells are threats to maintaining these crucial spawning beaches.
The content of this report summarizes the data acquired from July 2006 to June 2007 (with mention of spawning results to September 07).The above was ADAPTED FROM RAMONA de GRAAF’S reference materials and the Forage Fish Report The photos above come from the Power Point presentation of Emerald Sea Research and Consulting. FORAGE FISH REPORT  The Boundary Bay intertidal forage fish spawning habitat report. Please contact Ramona and Wen-Ling of Forage Fish Matter! at emeraldsearesearch(use the at sign)hotmail.com or rdegraaf(use the at sign)bms.bc.ca for more information, talks or training!

 

Googlethe PDF : Preliminary Habitat Assessment for suitability of intertidally spawning forage fish species, Pacific sand lance (Ammodytes hexapterus) and surf smelt (Hypomesus pretiosus) Esquimalt Lagoon, Colwood , British Columbia

ALSO RAMONA HAS DONE A BEACH SPAWNING REPORT