Weed Alert!
Glyceria declinata Brébiss.
(syn. Glyceria fluitans subsp. declinata (Brébiss.) O. Bolòs, Masalles, & Vigo,
G. fluitans var. declinata (Brébiss.) Ghisa,
G. notata subsp. declinata (Brébiss.) E.J. Weeda,
G. plicata subsp. declinata (Brébiss.) E.J. Weeda,
Glyceria plicata var. declinata (Brébiss.) Druce)
(Eurasian waxy mannagrass, small mannagrass, sweet grass)
Glyceria declinata has invaded deep vernal pools, swales, ditches, and stock ponds along the entire eastern side of California's Central Valley, from Shasta County south to Fresno County. It is also present in vernal pools in Mendocino County. It is adapted to long periods of inundation and typically grows from the Lolium multiflorum ring that lines the high water mark, to the bottom of the pools where Eleocharis, Eryngium, Psilocarphus, and Downingia are found.
Description:
Perennial, culms 10-45 cm long. Leaf-sheaths tubular for much of their length; ligule an eciliate membrane 4-9 mm long, acute;
leaf-blades flat, or conduplicate; 3-18 cm long; 1.5-8 mm wide. Leaf-blade surface smooth. Leaf-blade margins scabrous.
Panicle open; linear, or lanceolate; equilateral, or nodding; 4-30 cm long. Spikelets ascending, or appressed; solitary.
Glume apices obtuse. Lemma and palea apices dentate. (Summarized from [1].)
While G. declinata is described as a perennial species, all observations from the Central Valley of California indicate
that it is either an annual genotype or growing as a facultative annual. In the Central Valley the spikelets mature from
late April through May and shatter at maturity coating the ground below the plant with seed.
To the casual eye, G. declinata can easily be mistaken for the non-native Lolium multiflorum, as is illustrated
in the image above that shows both in the same photograph.
Scientific and Common Names:
The genus name Glyceria is derived from the Greek name for sweet, for the taste of the grain which is relished by
waterfowl and which has been harvested by humans for millennia.
Because the Jepson Manual [2] omits G. declinata and incorrectly describes the lemma tip of G. occidentalis
as jagged or irregular, there has been some confusion regarding whether G. declinata from the Central Valley is in
reality G. occidentalis. Glyceria declinata is correctly described in Munz [3]. Another complication with
correctly identifying Glyceria species is that the morphological characteristics used to identify them are very
similar and variable. As part of the development of the Poaceae section of The Flora of North America [4], Ian Wipple,
Mary Barkworth, and Shaun Bushman developed chloroplast molecular markers to help distinguish species among herbarium
collections of several Glyceria species [5]. They tested herbarium samples from Humboldt County, the Sierra Nevada
foothills, and a degraded vernal pool in Sacramento County and all samples were determined to be G. declinata. Using
their markers, Harald Meimberg and John Gerlach recently completed an analysis of six vernal pool populations from Sacramento County and
Stanislaus County and all populations were determined to be G. declinata (unpublished). From these two studies and from
observations of lemma characteristics of field samples from other counties, it appears that the only Glyceria species
present in the Central Valley is G. declinata.
Native Range:
Europe: northern, central, southwestern, southeastern, and eastern. Africa: Macaronesia.
Glyceria declinata is widespread in Europe and in areas with temperate climate it is considered a colonizer of mud
flats and banks along slow moving rivers and streams and along the shores of lakes and ponds. It generally grows in the less
inundated areas between the more inundation-tolerant G. fluitans and upland vegetation.
In the Mediterranean climate areas of Spain and Portugal G. declinata is often a dominant native species of vernal
pools [6] and playas and a weed of rice fields in Spain and Portugal where it appears to behave as an annual
species.
Range as an Invader:
In California, it is known to occur in Shasta, Tehama, Butte, Yuba, Placer, Sacramento, San Joaquin, Stanislaus, Fresno,
Mendocino Sonoma, Alameda, and counties. In the USA it is also recorded from Louisiana and New York [7].
It also occurs in Australia and New Zealand.
Reproduction and Methods of Dispersal:
Glyceria declinata was first identified in California in 1953 by Beecher Crampton from a plant he collected from
a vernal pool in Stanislaus County [8] and, according to vernal pool botanists [9], during the last twenty years it has
rapidly spread through rice fields, vernal pools, cattle ponds, and roadside ditches.
In 2001 during a vernal pool vegetation classification project, a survey crew found it in a large vernal pool on the Lane Ranch in San Joaquin County
but identified it as G. occidentalis [10]. In 2001, the cover of Glyceria in the pool was 2%. When John
Gerlach surveyed
the pool in May 2006 the plants had lemma morphology consistent with that of G. declinata and the cover was greater
than 90% in spite of being recently grazed. The extensive and complete cover and the lack of flowering native species
suggests that this is not just an annual fluctuation in population size.
Waterfowl are strongly attracted to maturing plants and strip the seed from the culms with their bills and they probably
function as primary long distance seed dispersal vectors (pers. observation). Seed dispersal by waterfowl has probably increased dramatically as
nonmigratory populations of Canada geese (Branta canadensis) have exploded in California during the last 20 years.
Humans and wildlife disperse the seed over shorter distances as seed readily adheres to wet pants and boots.
Impacts:
The invaded vernal pools are some of the most important natural resources in California and contain both federal and state
listed endangered plant and animal species. Dense G. declinata invasions appear to eliminate or significantly
reduce populations of all native annual plant species, such as endangered Orcuttia viscida (Sacramento orcutt grass)
from the vernal pools. It was rated a weed of "Moderate" impact by the California Invasive Plant Council [11].
Its population dynamics in vernal pools are erratic but it often establishes dense stands of large plants which both shade-out
endemic species and eliminate the bare ground they require for germination and establishment. It produces an enormous amount
of fine root mass on or just under the surface of the soil and a large leaf mass. These biomass changes probably effect
nutrient cycling in the vernal pools and negatively impact vernal pool hydrology through increased transpiration.
While it has been collected from rice fields in Butte County for 20 years, it has recently become problematic enough to be
considered a winter and spring weed and its dense populations make it more difficult to cultivate the fields for planting.
Control:
Control methods in vernal pools with sensitive status species will be a complex regulatory problem and field
eradication efforts will require
persistence. All methods should target existing seed and adult plants and reduce the spread of seed by animal and human
vectors. Hand weeding prior to spikelet shattering is effective for small populations in high value vernal pools and must
be continued annually until the seed bank is completely exhausted. Surrounding vernal pools and swales should also be weeded
to prevent the rapid reintroduction of seed. Reducing seed spread can be accomplished by excluding humans and domestic animals
from G. declinata populations from the beginning of spikelet shattering until all seed has been dropped and the
vernal pools are completely dry. It is critical that all equipment used in both natural and created vernal pools is
absolutely free of adhering seed or soil. Additionally, artificial ponds that attract waterfowl should be eliminated to
reduce site desirability. Stock ponds may need to be replaced with other water sources that do not attract waterfowl or
support G. declinata. Glyceria species are generally regarded as species with high soil and water fertility
requirements so precautions should be taken to prevent the addition of nutrients in any form.
References:
[1] Clayton, W.D., K.T. Harman, and H. Williamson (2006). World Grass Species: Descriptions, Identification, and Information
Retrieval. http://www.kew.org/data/grasses-db.html. (accessed 20 August 2006).
[2] Hickman, J.C. (ed.) (1993) The Jepson Manual: Higher Plants of California. University of California Press,
Berkeley.
[3] Munz, P.A. (and Keck, D.D.) (1968) A California Flora and Supplement. University of California Press, Berkeley.
[4] M.E. Barkworth (In preparation). Flora of North America.
[5] Whipple, I.G., M.E. Barkworth, B.S. Bushman (2006) Am. J. Bot. (submitted).
[6] J. A. Molina (1996). Sobre la vegetación del los humedales de la Peninsula Ibérica
(1. Phragmiti-Magnocaricetea). Lazaroa 16:27-88.
[7] Plants Database, http://plants.usda.gov. Accessed August 2006.
[8] University of California Davis Herbarium specimen UCD36270.
[9] L. Aheart, J. Dittes, C. Witham, pers. communication.
[10] Barbour, M.G., A.I. Solomeshch, R.F. Holland, C.W. Witham, R.L. Macdonald, S.S. Cilliers, J.A. Molina, J.J. Buck,
J.M. Hillman (2005).Vernal pool vegetation of California: communities of long-inundated deep habitats. Phytocoenologia
35: 177-200.
[11] http://portal.cal-ipc.org/files/PAFs/Glyceria%20declinata.pdf
--John Gerlach/Environmental Science Associates
--Edited: Barry Rice/Global Invasive Species Team; August 2006