Holcus lanatus

L.

Common Velvet Grass

GNRUnranked Found in 40 roadless areas NatureServe Explorer →
GNRUnrankedGlobal Rank
Identity
Unique IDELEMENT_GLOBAL.2.151209
Element CodePMPOA37010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
KingdomPlantae
PhylumAnthophyta
ClassMonocotyledoneae
OrderCyperales
FamilyPoaceae
GenusHolcus
Other Common Names
Common Velvetgrass (EN) common velvetgrass (EN) Houlque laineuse (FR)
Concept Reference
Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Conservation Status
Change Date1994-03-22
Edition Date1988-11-21
Edition AuthorsDON PITCHER, MARY J. RUSSO (Revision), CAFO
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Range Extent Comments
Velvet grass is of European origin, its center of origin thought to be the Iberian peninsula (Jacques and Munro 1963), and is a native of temperate areas of Europe and Asia (Scoggan 1978). It was probably introduced to North America either accidentally as a contaminant of forage seed or deliberately as a component of seed mixtures for meadow (Thompson and Turkington 1988). It has since spread and become locally abundant from British Columbia to Nova Scotia, Canada, south from Maine to Kansas and Colorado, south to Georgia and Louisiana and in primarily moist areas below 7500 feet along the Pacific Coast from British Columbia to California and to Montana and Arizona (Thompson and Turkington 1988).

Velvet grass is common throughout Europe except the extreme north and northeast where it is only casual (Thompson and Turkington 1988). In England, it is widely distributed in fields, partic- ularly on north-facing slopes (Grime and Lloyd 1973). The grass is now found throughout Asia, Africa, New Zealand, Australia, and sub- Antarctic islands. It has escaped cultivation and become a weed pest along roadsides, fencerows, ditch banks, in old pastures, and other disturbed sites, particularly in moist places (Muenscher 1955). In the Coast Ranges, it has become a weed of minor importance (Robbins et al. 1970).
Threat Impact Comments
HOLCUS LANATUS is present on Oregon and Washington westside grassland preserves and the Northern Califoria Coast Range Preserve. It is apparently not a major problem species on Nature Conservancy lands in California, but where it occurs, control may be difficult due to its prolific seeding ability and its possible allelopathic effect on native grasses. It has, however, become a major problem on western Oregon and Washington grassland preserves.
Ecology & Habitat

Diagnostic Characteristics

HOLCUS LANATUS is rarely mistaken for any other species with the possible exception of H. MOLLIS. H. LANATUS can be distinguished by the purplish coloration on the panicles and veins of the sheaths, soft hairs all over, and lack of rhizomes. The two species may be able to hybridize (Jones 1954).

Habitat



HOLCUS LANATUS exhibits a wide climatic tolerance of temperate regimes over a wide range of altitudes (0-1500m). It is killed by severe frost (Watt 1978b). Optimal growth occurs under moist conditions; however, it grows well in very wet conditions and can survive moderate periods of drought (Watt 1978a).

In Britain H. LANATUS occurs on a wide range of soil types including those of rich-fen and fen-meadow communities, poorly drained, waterlogged, low to moderately fertile, and nutrient-rich soils. It occurs independent of soil phosphorous content and grows well in potassium- and/or nitrogen-poor soils. It tolerates a wide range of soil pH, growing best between pH 5.0 and 7.5 (Thompson and Turkington 1988). Studies in Oregon (Hart and McGuire 1963) indicate an increase in the abundance of velvet grass under mildly acidic conditions.

Ecology

Little research has been done on HOLCUS LANATUS in North America. In Europe, it is an adaptable, competitive species that tolerates a wide range of habitats, particularly acidic, low nutrient sites (Watt 1977).

GROWTH, PRODUCTIVITY, AND COMPETITION

In the Soviet Union, Trapaidze and Gogiya (1981) report that HOLCUS species have an exceptionally long growing season. Germination occurs from seed or as sprouts from roots in late autumn, with flowering between May and July. In a Dutch experiment (van Andel and Jager 1981), velvet grass leaf area peaked 15 weeks after sowing, and maximum dry weight was attained two weeks later. In the later stages of growth, root mass increased dramatically, reaching half of the total plant weight. Nitrogen levels also showed a marked increase after 15 weeks of growth. Nitrogen availability may be the limiting factor in HOLCUS LANATUS growth (Watt 1978). HOLCUS LANATUS normally occurs on soils of moderate to low fertility, but fertilization appears to improve its competitive ability (Remison and Snaydon 1980).

High water table levels reduce the productivity of velvet grass. HOLCUS manages to persist on these wet sites by producing a large number of fine roots on the soil surface where aeration and nutrient levels are higher (Watt and Haggar 1980b). Grootjans (1979) noted that a lowered water table increase the N-mineraliza- tion rate and the nitrate content leading to a strong site dominance by HOLCUS LANATUS. Severe winter weather and high ground water can kill the grass, perhaps by lowering the N-mineralization rate (Bakker et al. 1980). Velvet grass can tolerate soils with a pH range of 3 to 8.1 (Grime and Lloyd 1973) but does best on sites with a pH of 4.5 to 5.5 (Roberts 1982).

Like other weeds from disturbed but productive habitats, HOLCUS LANATUS is able to grow rapidly. The mean recorded growth rate is 1.56 g/g.week while the maximum growth rate exceeds 2 g/g.week (Redosevich and Holt 1984). This rapid growth may indicate a high potential competitive ability among crop and weed species (Redosevich and Holt 1984). This aggressiveness is shown in the dominance of velvet grass in English pastures (Turkington et al. 1979). HOLCUS also does well in both high and low levels of light (Anonymous 1976).

In an English study, Remison and Snaydon (1980) found that HOLCUS LANATUS outcompeted DACTYLIS GLOMERATA (orchard grass) under a wide variety of conditions. Velvet grass yield increased by 50% on sites with competition over sites where it was grown alone. Similar results are reported for competition between HOLCUS LANATUS and LOLIUM PERENNE (ryegrass). Velvet grass is particularly aggressive in root competition due to its higher proportion of roots than other British pasture species (Watt and Haggar 1980a).

In a Dutch grassland study (Bakker et al. 1980), HOLCUS LANATUS became dominant when the grass was mowed following maturation and seed dispersal. When earlier cuts were made, HOLCUS LANATUS survived but became less dominant. HOLCUS LANATUS responds well to cutting, even when cut back to only 2 cm above the ground. On unharvested sites, velvet grass gradually forces other plants out, reducing species diversity. This process is particularly apparent on unfertilized sites. Allelopathy may also play a role in the dominance of HOLCUS LANATUS over other grasses (Remison and Snaydon 1978).

Reproduction

FLORAL BIOLOGY

In North America, flowering occurs June through August (Septem- ber). H. LANATUS is wind pollinated and predominantly an outcrossing species. Successful self-fertilization occurs only occasionally and is impossible in some plants (Beddows 1931). During anthesis the panicle opens from the apex down and closes likewise (Tutin et al. 1964).

SEED PRODUCTION

In England, HOLCUS LANATUS seeds are shed from June to September (Mortimer 1976). The plants require vernalization to flower, but this process is enhanced and, to a small extent, replaced by short- day treatment (Watt 1977). It flowers and produces seeds from the second year onwards and behaves as a "paucennial." In places with reduced competition, the plant will often die after a few years, particularly following luxuriant flowering. In southern Europe, very short-lived races that flower the first year are found in dry habitats. In northern races, the plants require a period of vegetative growth prior to flowering in the second year (Bocher and Larsen 1958). HOLCUS LANATUS also exhibits variation in culm length and growth habit. In exposed maritime habitats, it grows as a low plant, while farther inland, the plants are more erect with tall culms (Bocher and Larsen 1958).

Trapaidze and Gogiya (1981) report up to 850 wind-dispersed seeds per plant in the Soviet Union. In England, Watt (1976) found production of up to 240,000 seeds per plant, most of which germinated shortly after landing on moist soils.

SEED GERMINATION

Williams (1983) found that when stored under dry, shaded conditions, velvet grass seeds remained viable for at least 48 weeks with 90-99% germination. Trapaidze and Gogiya (1981) found a germination rate of 95% for the first two years after seed harvest. Both vertebrates and earthworms appear to significantly reduce velvet grass populations by their burial or consumption of seeds (Mortimer 1976). When the seeds were buried, only 3% of them were still viable after a year. Seeds buried at a depth of 1-2 cm had a much higher chance of emergence than those at a depth of 3 cm (Williams 1983). In the Soviet Union, HOLCUS seeds showed 87% germination rate on the ground surface, 76% at a depth of 1 cm, and only 5% germination at 2 cm (Trapaidze and Gogiya 1981). HOLCUS LANATUS seeds are thus apparently not innately dormant, though certain field conditions may enforce dormancy (Williams 1983). Even though most of the seeds are nondormant, the potential number of seeds produced by each plant is so high that even a 1% level of innate or enforced dormancy would result in a large amount of buried viable seed (Watt 1976). The species can thus exist in large numbers in a seed bank, even if it is not an important plant on a given site (Roberts 1982).

Seed germination can occur at 7-8 C (Trapaidze and Gogiya 1981). Thompson and Whatley (1984) suggest that burying the seeds may induce a requirement for fluctuating temperatures of greater than 19 C. The result is that HOLCUS LANATUS seeds germinate more readily in larger canopy gaps (wider than 25 cm) where their survival chances are improved (Thompson 1977). Mortimer (1976) estimates that when various mortality factors are taken into consideration, each HOLCUS LANATUS plant can produce 9.9 adult plants the following year.

HOLCUS LANATUS is not usually considered a stoloniferous species, but regeneration can occur by the formation of decumbent tillers in late summer that subsequently produce roots and shoots at the nodes. Growth of these shoots may be enhanced by grazing or mowing, but root growth does not appear to be affected (Watt and Haggar 1980a).
Terrestrial Habitats
Grassland/herbaceousUrban/edificarian
Palustrine Habitats
SCRUB-SHRUB WETLANDBog/fen
Other Nations (2)
United StatesNNA
ProvinceRankNative
New YorkSNANo
MaineSNANo
MichiganSNANo
MontanaSNANo
North DakotaSNANo
MassachusettsSNANo
OklahomaSNANo
IndianaSNANo
UtahSNANo
District of ColumbiaSNANo
ConnecticutSNANo
New JerseySNANo
PennsylvaniaSNANo
ArizonaSNANo
AlabamaSNANo
DelawareSNANo
MarylandSNANo
OregonSNANo
Rhode IslandSNANo
VermontSNANo
OhioSNANo
GeorgiaSNANo
TexasSNANo
LouisianaSNANo
IdahoSNANo
IllinoisSNANo
KansasSNANo
AlaskaSNANo
South CarolinaSNANo
WisconsinSNANo
TennesseeSNANo
MissouriSNANo
ArkansasSNANo
New MexicoSNANo
West VirginiaSNANo
HawaiiSNANo
IowaSNANo
CaliforniaSNANo
ColoradoSNANo
NevadaSNANo
MississippiSNANo
KentuckySNANo
North CarolinaSNANo
WashingtonSNANo
VirginiaSNANo
New HampshireSNANo
CanadaNNA
ProvinceRankNative
Island of NewfoundlandSNANo
British ColumbiaSNANo
QuebecSNANo
Nova ScotiaSNANo
OntarioSNANo
New BrunswickSNANo
Plant Characteristics
DurationPERENNIAL, SUMMER-FLOWERING
Economic Value (Genus)No
Roadless Areas (40)
California (8)
AreaForestAcres
Bald RockPlumas National Forest4,675
Barker ValleyCleveland National Forest11,940
Mt. Shasta BShasta-Trinity National Forest2,809
PaiuteInyo National Forest58,712
RinconSequoia National Forest54,610
Slate Mtn.Sequoia National Forest12,299
SugarloafSan Bernardino National Forest8,206
Timbered CraterLassen National Forest4,096
North Carolina (8)
AreaForestAcres
BearwallowPisgah National Forest4,113
Craggy MountainPisgah National Forest2,657
Graveyard Ridge (addition)Pisgah National Forest1,958
Laurel MountainPisgah National Forest5,683
Middle Prong AdditionPisgah National Forest1,852
Sam Knob (addition)Pisgah National Forest2,576
SnowbirdNantahala National Forest8,489
South Mills RiverPisgah National Forest8,588
Oregon (13)
AreaForestAcres
Drift CreekSiuslaw National Forest6,333
LarchMt. Hood National Forest12,961
Menagerie (rooster Rock)Willamette National Forest374
Moose LakeWillamette National Forest5,013
North PaulinaDeschutes National Forest19,670
Roaring RiverMt. Hood National Forest27,316
Sky Lakes AWinema National Forest3,940
South KalmiopsisSiskiyou National Forests104,477
South PaulinaDeschutes National Forest9,074
TahkenitchSiuslaw National Forest5,799
TenmileSiuslaw National Forest10,818
Umpqua SpitSiuslaw National Forest2,090
WoahinkSiuslaw National Forest5,309
Tennessee (1)
AreaForestAcres
Flint Mill GapCherokee National Forest9,494
Virginia (2)
AreaForestAcres
Mt. PleasantGeorge Washington National Forest8,933
North MountainJefferson National Forest8,377
Washington (2)
AreaForestAcres
Glacier Peak KMt Baker-Snoqualmie National Forest47,269
South QuinaultOlympic National Forest11,081
West Virginia (6)
AreaForestAcres
Cranberry AdditionMonongahela National Forest11,123
Cranberry Glades Botanical AreaMonongahela National Forest785
Dry ForkMonongahela National Forest657
Falls Of Hills CreekMonongahela National Forest6,925
Seneca CreekMonongahela National Forest22,287
Turkey MountainMonongahela National Forest6,421
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