Plant Assessment Form
More Mesembryanthemum nodiflorum resources
Mesembryanthemum nodiflorum
Synonyms: Cryophytum nodiflorum; Gasoul nodiflorum; Aridaria paucandra; Cryophytum gibbosum; Cryophytum rogersii
Common Names: slenderleaf iceplant; small flowered iceplant
Evaluated on: 22-Dec-16
List committee review date: 26/01/2017
Re-evaluation date:
Evaluator(s)
Cal-IPC
916-802-2004
rrobison@cal-ipc.org
List committee members
Jutta BurgerNaomi Fraga
Denise Knapp
Chris McDonald
Ron Vanderhoff
John Knapp
Elizabeth Brusati
General Comments
No general comments for this species
Table 2. Criteria, Section, and Overall Scores
Overall Score?
Limited
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Alert Status?
No Alert
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Documentation?
3.5 out of 5
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Score | Documentation | |||
1.1 | ?Impact on abiotic ecosystem processes | B. Moderate | Reviewed Scientific Publication | |
1.2 | ?Impact on plant community | B. Moderate | Reviewed Scientific Publication | |
1.3 | ?Impact on higher trophic levels | C. Minor | Reviewed Scientific Publication | |
1.4 | ?Impact on genetic integrity | D. None | Reviewed Scientific Publication | |
2.1 | ?Role of anthropogenic and natural disturbance in establishment | B. Moderate | Reviewed Scientific Publication | |
2.2 | ?Local rate of spread with no management | C. Stable | Observational | |
2.3 | ?Recent trend in total area infested within state | C. Stable | Observational | |
2.4 |
?Innate reproductive potential (see Worksheet A) |
B. Moderate | Reviewed Scientific Publication | |
2.5 | ?Potential for human-caused dispersal | C. Low | Reviewed Scientific Publication | |
2.6 | ? Potential for natural long-distance dispersal | C. Rare | Reviewed Scientific Publication | |
2.7 | ?Other regions invaded | C. Already invaded | Reviewed Scientific Publication | |
3.1 |
?Ecological amplitude/Range (see Worksheet C) |
A. Widespread | Reviewed Scientific Publication | |
3.2 |
?Distribution/Peak frequency (see Worksheet C) |
D. Very low | Reviewed Scientific Publication |
Table 3. Documentation
Scores are explained in the "Criteria for Categorizing Invasive Non-Native Plants that Threaten Wildlands".
Section 1: Impact | |
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Question 1.1 Impact on abiotic ecosystem processes? | B Reviewed Scientific Publication |
Identify ecosystem processes impacted: Mesembryanthemum crystallinum and M. nodiflorum are salt accumulators. After plant death, the salt leaches from the decaying plant into the surrounding soil. This increased salinity stops other, less salt-tolerant species from establishing. More information is available on salt accumulation by M. crystallinum than for M. nodiflorum, but it is assumed that the mechanisms and ecosystem results are similar for both species. Sources of information: El-Ghareeb 1991 |
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Question 1.2 Impact on plant community composition, structure, and interactions? |
B Reviewed Scientific Publication |
Identify type of impact or alteration: Excluding native plants, possibly altering soil conditions (see Question 1.1). On Santa Barbara Island, crystalline iceplant, Mesembryanthemum crystallinum, forms large, dense patches and accumulates salt to the extent that all other species are generally excluded. A common associate is another annual iceplant, Mesembryanthemum nodiflorum. This is a serious management problem because only periodically are salt-tolerant shrubs such as Suaeda californica able to establish, if they can overtop the iceplant rapidly enough to overcome the shading effects. Otherwise, the iceplant leads to the extirpation of other plants from the area and then to erosion problems (Halvorson 1992). On the Channel Islands, M. nodiflorum is found in bare areas along the coastline extending in 1/4 mile. These sites are known locations of several rare and federally listed Malacothrix species (Knapp, J. pers. comm.). Knapp and Garoutte (2016) found a strong negative impact of Mesembryanthemum crystallinum on native plant diversity and (related) arthropod diversity at two of three study sites on San Nicolas Island. Sources of information: Halvorson 1992 in Stone 1992. |
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Question 1.3 Impact on higher trophic levels? | C Reviewed Scientific Publication |
Identify type of impact or alteration: Causes oxalate poisoning in sheep. Ice plant was a primary food item for island foxes (>10% frequency of occurrence in scats) during two seasons on San Clemente, three seasons on San Miguel and all four seasons on San Nicolas. Although these plants are providing a benefit to foxes by increasing the diversity of available food items, these plants also may be excluding native species. Reducing or eliminating these non-native plants probably could be conducted without adverse impacts to foxes, with the exception of San Nicolas. On this island, foxes may be at least partially dependent on these species and any reductions should be conducted gradually and preferably in conjunction with active restoration of native species to provide alternate foods for foxes (Cypher 2010). Knapp and Garoutte (2016) found a strong negative impact of Mesembryanthemum crystallinum on native plant diversity and (related) arthropod diversity at two of three study sites on San Nicolas Island. Sources of information: Cypher 2010 |
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Question 1.4 Impact on genetic integrity? | D Reviewed Scientific Publication |
There are no native species in the Mesembryanthemum genus which M. nodiflorum could hybridize with in California. There are a few native species in the Aizoaceae, but not in the Mesembryanthemum genus. Sources of information: Jepson eFlora 2016 |
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Section 2: Invasiveness | |
Question 2.1 Role of anthropogenic and natural disturbance in establishment? |
C Observational |
Describe role of disturbance: M. chrystallinum needs open disturbed areas for establishment and does not grow well in intact grassland. It is assumed that M. nodiflorum has similar requirements. Sources of information: Vivrette and Muller 1977 |
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Question 2.2 Local rate of spread with no management? | C Observational |
Describe rate of spread: In the south coastal region this species has been present for a century or more with numerous collections and records over that period. During this period it has colonized much or most of the suitable habitat (saline coastal bluff and bluff scrub on packed, exposed soils). At its current level of establishment I suggest, at least in this region, that it may be difficult to assess its rate of spread, since it has already filled much of the suitable habitat (Vanderhoff, pers. comm.). In inland southern California it is not as invasive as along the coast, but it is fairly common (Fraga, pers. comm.). Sources of information: Fraga, N. Personal communication. |
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Question 2.3 Recent trend in total area infested within state? | C Observational |
Describe trend: In the south coastal region this species has been present for a century or more with numerous collections and records over that period. During this period it has colonized much or most of the suitable habitat (saline coastal bluff and bluff scrub on packed, exposed soils). At its current level of establishment I suggest, at least in this region, that it may be difficult to assess its rate of spread, since it has already filled much of the suitable habitat (Vanderhoff, pers. comm. Knapp, J. pers. comm.). On the Channel Islands it is stable and has reached its distribution (J. Knapp, pers. comm.). Sayers reports seeing more in San Luis Obispo area recently. Sources of information: Knapp, J. Personal communication. |
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Question 2.4 Innate reproductive potential? | B Reviewed Scientific Publication |
Describe key reproductive characteristics: M. nodiflorum reproduces by seed. Seeds are produced in winter after rains. In California flowering occurs from March to August. During the first few years after seed maturation, the seeds are in a state of primary dormancy and none germinate. In its native habitat, M. nodiflorum seeds adhere to the soil and become part of the soil surface crust for many years until they germinate. Germination is regulated by the amount of rain that dilutes the salts that accumulate near the soil surface. There is no information available on vegetative reproduction or spread of M. nodiflorum, but since it is an annual species it is assumed to not reproduce vegetatively (Vanderhoff, pers. comm.). Sources of information: Calflora 2016 |
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Question 2.5 Potential for human-caused dispersal? | C Reviewed Scientific Publication |
Identify dispersal mechanisms: M. crystallinum is used for landscaping by Caltrans and by gardeners and can invade areas disturbed by grazing. M. crystallinum, and it is assumed M. nodiflorum, are able to invade disturbed areas created by human activities. M. nodiflorum is not commonly available horticulturally, but seeds are available on-line. Sources of information: Randall 2000 |
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Question 2.6 Potential for natural long-distance dispersal? | C Reviewed Scientific Publication |
Identify dispersal mechanisms: Seeds are dispersed by water and adhere to the soil surface. The reference (Gutterman and Gendler 2005) does not list the distance traveled. M. crystallinum is dispersed by rabbits and mice, so that could occur with M. nodiflorum. Sources of information: Gutterman and Gendler 2005. |
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Question 2.7 Other regions invaded? | C Reviewed Scientific Publication |
Identify other regions: M. nodiflorum is native to South Africa. Other regions invaded are in Oregon, Arizona, Mexico, Europe and southern Australia. In Australia, Mesembryanthemum crystallinum and M. nodiflorum are found on wide range of soil types, from well-drained sandy soils (including sand dunes), to loams and clays. They prefer acid, neutral or alkaline soils, but can tolerate nutritionally poor or saline soils. They occur in a range of vegetation communities, including saltmarsh, samphire flats eucalypt woodlands and shrublands, and as with many introduced species, also grow in disturbed sites such as roadsides, rubbish dumps and homestead yards. In California, M. nodiflorum is found in coastal bluffs, salty flats in the interior of the coastal slopes, and saline wetland margins, areas which are similar to those invaded in Australia and elsewhere. The Pacific Islands in Mexico within the California Floristic Province is invaded in the same habitat types as the Channel Islands (Knapp, J. pers. comm.). Sources of information: DiTomaso and Healy 2007 |
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Section 3: Distribution | |
Question 3.1 Ecological amplitude/Range? | A Reviewed Scientific Publication |
In California, M. nodiflorum is found in coastal bluffs, salty flats in the interior of the coastal slopes, and saline wetland margins. It occurs in coastal, inland and desert habitats from San Diego north to the San Francisco Bay Area, with one outlying population in Glenn County. The first herbarium specimen in California was collected in 1882 in San Diego. Based on specimens in CCH, appears to have first been introduced along the coast and on the Channel Islands, then spread inland along roads in the 1960s and 70s, and began being collected inland in the 1990s. In inland Southern California its around in the usual low alkaline places, in western Riverside County. Populations are scattered and typically not terribly large, but can be locally fairly common. Its in the Perris Basin and on the alkaline flats west of Hemet mostly, but some in the Elsinore-Temescal area. In open sites, seasonally wet, fine alkaline clay soils (Sanders, pers. comm). Also observed around Lake Elsinore in semi-saline soils of the dry lakebed, and along the outlet drainage down into Temescal Canyon (Boyd, pers. comm.). Also seen along riparian corridors along the Santa Clara River in Ventura County (Fraga, pers. comm.). Invades the Pacific Islands in Mexico within the California Floristic Province (Knapp, J. pers. comm.). Sources of information: DiTomaso and Healy 2007 |
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Question 3.2 Distribution/Peak frequency? | D Reviewed Scientific Publication |
Describe distribution: In California, M. nodiflorum is found in coastal bluffs, salty flats in the interior of the coastal slopes, and saline wetland margins. It occurs in coastal, inland and desert habitats from San Diego north to the San Francisco Bay Area, with one outlying population in Glenn County. In all cases it occupies < 5% of the area of that ecological type in California. Sources of information: Calflora 2016 |
Worksheet A - Innate reproductive potential
Reaches reproductive maturity in 2 years or less | Yes |
Dense infestations produce >1,000 viable seed per square meter | Unknown |
Populations of this species produce seeds every year. | Yes |
Seed production sustained over 3 or more months within a population annually | Unknown |
Seeds remain viable in soil for three or more years | Yes |
Viable seed produced with both self-pollination and cross-pollination | Unknown |
Has quickly spreading vegetative structures (rhizomes, roots, etc.) that may root at nodes | No |
Fragments easily and fragments can become established elsewhere | No |
Resprouts readily when cut, grazed, or burned | Unknown |
Total points: | 4 |
Total unknowns: | 4 |
Total score: | B? |
Related traits:
There is no specific information on the vegetative spread of M. nodiflorum. Populations of this species produce seeds every year (Knapp, J. pers. comm.).
Worksheet B - Arizona Ecological Types is not included here
Worksheet C - California Ecological Types
(sensu Holland 1986)Major Ecological Types | Minor Ecological Types | Code? |
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Marine Systems | marine systems | |
Freshwater and Estuarine | lakes, ponds, reservoirs | |
Aquatic Systems | rivers, streams, canals | |
estuaries | ||
Dunes | coastal | D, < 5% |
desert | ||
interior | ||
Scrub and Chaparral | coastal bluff scrub | D, < 5% |
coastal scrub | D, < 5% | |
Sonoran desert scrub | ||
Mojavean desert scrub (incl. Joshua tree woodland) | ||
Great Basin scrub | ||
chenopod scrub | ||
montane dwarf scrub | ||
Upper Sonoran subshrub scrub | ||
chaparral | ||
Grasslands, Vernal Pools, Meadows, and other Herb Communities | coastal prairie | D, < 5% |
valley and foothill grassland | ||
Great Basin grassland | ||
vernal pool | ||
meadow and seep | ||
alkali playa | D, < 5% | |
pebble plain | ||
Bog and Marsh | bog and fen | |
marsh and swamp | ||
Riparian and Bottomland habitat | riparian forest | |
riparian woodland | ||
riparian scrub (incl.desert washes) | ||
Woodland | cismontane woodland | |
piñon and juniper woodland | ||
Sonoran thorn woodland | ||
Forest | broadleaved upland forest | |
North Coast coniferous forest | ||
closed cone coniferous forest | ||
lower montane coniferous forest | ||
upper montane coniferous forest | ||
subalpine coniferous forest | ||
Alpine Habitats | alpine boulder and rock field | |
alpine dwarf scrub | ||
Amplitude (breadth): | B | |
Distribution (highest score): | D |
Infested Jepson Regions
Click here for a map of Jepson regions
- CA Floristic Province
- Central West
- Great Valley
- Southwest
- Desert Province
- Mojave Desert
- Sonoran Desert