Plant Assessment Form
More Geranium purpureum resources
Geranium purpureum
Synonyms: Geranium robertianum subsp. purpureum; Pelargonium purpureum
Common Names: little robin
Evaluated on: 27-Dec-16
List committee review date: 25/01/2017
Re-evaluation date:
Evaluator(s)
Cal-IPC
916-802-2004
rrobison@cal-ipc.org
List committee members
Elizabeth BrusatiTim Hyland
Eric Wrubel
Irina Irvine
Holly Forbes
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 out of 5
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Score | Documentation | |||
1.1 | ?Impact on abiotic ecosystem processes | U. Unknown | No Information | |
1.2 | ?Impact on plant community | C. Minor | Observational | |
1.3 | ?Impact on higher trophic levels | D. Negligible | Reviewed Scientific Publication | |
1.4 | ?Impact on genetic integrity | C. Minor/Low | Reviewed Scientific Publication | |
2.1 | ?Role of anthropogenic and natural disturbance in establishment | B. Moderate | Observational | |
2.2 | ?Local rate of spread with no management | A. Increases rapidly | Observational | |
2.3 | ?Recent trend in total area infested within state | A. Increasing rapidly | 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 | A. Invades 3 or more ecological types | Reviewed Scientific Publication | |
3.1 |
?Ecological amplitude/Range (see Worksheet C) |
A. Widespread | Other Published Material | |
3.2 |
?Distribution/Peak frequency (see Worksheet C) |
D. Very low | Other Published Material |
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? | U No Information |
Identify ecosystem processes impacted: There is no information available on G. purpureum's impact on abiotic ecosystem processes. This question is scored as Unknown based on lack of reported abiotic effects. Sources of information: |
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Question 1.2 Impact on plant community composition, structure, and interactions? |
C Observational |
Identify type of impact or alteration: "Geranium purpureum is a major player that has taken over Sonoma Valley. I have a drainage at the Bouverie Preserve which had a small patch 4 years ago. The following year it had expanded to several acres, and several new occurrences. I find it to be much more invasive than G. robertianum, which has infested all 4 canyons of Bolinas Lagoon Preserve but never forms the thick stands of G. purpureum" (Gluesenkamp pers comm.). Sources of information: Gluesenkamp, D. Personal communication. |
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Question 1.3 Impact on higher trophic levels? | D Reviewed Scientific Publication |
Identify type of impact or alteration: There is no information available on G. purpureum's impact on higher trophic levels. Herrera (1991) found that 90% of experimental G. purpureum transplants exposed to vertebrate herbivores (cattle, red deer Cervus elephas, fallow deer Dama dama and rabbits Oryetolagus cunic ulus) were consumed well before reaching reproductive size whereas 60% of transplants protected from grazing set at least one fruit. Sources of information: Herrera 1991 |
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Question 1.4 Impact on genetic integrity? | C Reviewed Scientific Publication |
G. purpurem can self pollinate as well as cross pollinate. There is no documentation of it hybridizing with native Geranium species in California. Only two native California Geranium species -- Geranium bicknellii and Geranium carolinianum -- overlap with the current range of G. purpureum and could potentially hybridize. There are also many more non-native geraniums occurring in these areas (such as G. dissectum) which would be more likely to hybridize with natives and cause population changes. Sources of information: Calflora 2016 |
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Section 2: Invasiveness | |
Question 2.1 Role of anthropogenic and natural disturbance in establishment? |
A Observational |
Describe role of disturbance: Anecdotal information on G. purpureum establishment and dispersal in California is available. It has become one of the more abundant weeds along roadsides in Sonoma County, especially in urban areas, but also sporadically on lesser traveled rural byways. Trails are not exempt, as I’ve seen populations in many parks and open space areas (locally) spread from along trails to more remote woodlands (Warner pers. comm.). I have seen it in oak woodlands, riparian woodlands and in ruderal settings. It’s a common and difficult garden weed. I have no recollection of it showing up in chaparral (Rugyt, pers. comm.). Based on these observations and on the establishment of other invasive Geranium species such as G. dissectum and G. molle, which are facilitated by disturbance, and G. robertianum which does not require disturbance to establish, the species is given a Moderate rating. Sources of information: Cal-IPC PAF for G. dissectum, G. molle and G. robertianum. |
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Question 2.2 Local rate of spread with no management? | A Observational |
Describe rate of spread: Local rate of spread of G. purpureum in California without management appears to be high based on the following: Geranium purpureum is a major player that has taken over Sonoma Valley. I have a drainage at the Bouverie Preserve which had a small patch 4 years ago. The following year it had expanded to several acres, and several new occurrences (Gluesenkamp, pers. comm.) Sources of information: Gluesenkamp, D. Personal communication. |
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Question 2.3 Recent trend in total area infested within state? | A Observational |
Describe trend: Local rate of spread of G. purpureum in California without management appears to be high based on reports from regional experts. Where I have seen it, I would say Geranium purpureum is doubling in the East Bay hills, and increasing, but less rapidly near the coast in Golden Gate NRA, and Point Reyes NS (Wrubel, pers. comm.). Ruygt reports it as spreading less rapidly in Napa and Warner reports it as doubling in 10 years in Sonoma County (Ruygt and Warner, pers. comms.), so the highest rate of spread is selected for this question. Sources of information: Gluesenkamp, D. Personal communication. |
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Question 2.4 Innate reproductive potential? | B Reviewed Scientific Publication |
Describe key reproductive characteristics: Reproduces by seed and is an annual or biennial so produces seed in one or two years. Flowers in California from March to October (Rugyt pers. comm.). In Spain, peak flowering occurs in March and seed dispersal and senescence in May. Based on studies in Europe, It appears plants flower and set seed rapidly after germination but do not have a long flowering period. Seeds appear to have short dormancy and germinate as soon as winter starts. Seeds sown in the autumn in Britain germinate soon afterwards. No scarification is required. Seed production per flower is low -- one study found that many flowers produced fewer than 5 viable seeds. Geranium can facultatively self-pollinate, which it regularly does. Seeds remain viable for at least 7 years. Sources of information: Calflora 2016 |
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Question 2.5 Potential for human-caused dispersal? | C Reviewed Scientific Publication |
Identify dispersal mechanisms: Human-caused dispersal is not well documented. No information in the literature except for a description of it spreading rapidly along railroad lines in Germany. I suspect herbivores are involved in distribution but abundance can be attributed to high seed production and seed viability (Ruygt, pers. comm.). I’ve seen populations in many parks and open space areas (locally) spread from along trails to more remote woodlands — I suspect seeds are dispersed readily by numerous dispersers, especially humans, but likely including wildlife, bicycles, and horses (Warner, pers. comm.). Sources of information: Baltisberger and Waser-Walter 2009 |
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Question 2.6 Potential for natural long-distance dispersal? | C Reviewed Scientific Publication |
Identify dispersal mechanisms: Geranium seeds lack obvious adaptations promoting dispersal through wind or water. Seed collecting by ants has never been observed (Herrera 1991). Sources of information: Herrera 1991 |
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Question 2.7 Other regions invaded? | A Reviewed Scientific Publication |
Identify other regions: G. purpureum native to Europe, northern Africa, and western Asia and is alien in South America, New Zealand, and southern Africa (Jepson eFlora). It is also noted as spreading along railroad lines in Germany. There is little information on the habitat types which G. purpureum has invaded outside its native range. Within its native range it occurs on exposed shale near the coast and inland in a variety of habiats, in dry or moist soils in protected and unprotected areas. This indicates that there are probably ecological types in California which it has not yet invaded, based on its native distribution. The geographical distribution of Geranium purpureum is essentially Mediterranean, although a finger reaches through France to south-western England and southern Ireland while there are populations at elevations up to 7000 ft. in the mountains of eastern Africa and in Macaronesia and the Azores. This species has been introduced into South America where it is found established in comparable climatic conditions on the east and west coasts and even in the Juan Fernandez islands (Baker 1957). It is also noted as currently spreading in Northwestern and Central Europe (Eliáš 2011). Sources of information: Jepson eFlora |
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Section 3: Distribution | |
Question 3.1 Ecological amplitude/Range? | A Other Published Material |
G. purpureum was first collected in Napa county in 1976, and was not collected elsewhere in the Bay Area until the 1990s. It was collected in Butte County starting in 2008 and in Santa Cruz County in 2013, indicating its spread outward from Napa and the Bay Area. There is not a lot of information on the types of habitats that G. purpureum occurs in. Descriptions appear to be for oak woodland and grasslands, as well as urban areas and roadsides. Noted as spreading rapidly in riparian and woodland of inner North Coast ranges of California (Gluesenkamp, pers. comm.). It grows in mixed hardwood conifer forest where previously cover was sparse and primarily duff. It occurs from Carneros Valley area to Calistoga on the west range of Napa Valley, along the Napa River and more locally in the eastern part of the county. I have not seen it on the east side of Lake Berryessa. I have seen it in oak woodlands, riparian woodlands and in ruderal settings (Rugyt pers. comm.). Sources of information: CCH 2016 |
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Question 3.2 Distribution/Peak frequency? | D Other Published Material |
Describe distribution: G. purpureum occurs in 10 counties in California and is noted to be spreading rapidly in oak woodlands, riparian woodlands and in ruderal settings (Rugyt pers. comm.). However, the proportion of these community types overall throughout California is < 5%. Sources of information: CCH 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 | No |
Populations of this species produce seeds every year. | Yes |
Seed production sustained over 3 or more months within a population annually | No |
Seeds remain viable in soil for three or more years | Yes |
Viable seed produced with both self-pollination and cross-pollination | Yes |
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 | No |
Total points: | 5 |
Total unknowns: | 0 |
Total score: | B? |
Related traits:
Worksheet B - Arizona Ecological Types is not included here
Worksheet C - California Ecological Types
(sensu Holland 1986)Major Ecological Types | Minor Ecological Types | Code? |
---|---|---|
Marine Systems | marine systems | |
Freshwater and Estuarine | lakes, ponds, reservoirs | |
Aquatic Systems | rivers, streams, canals | |
estuaries | ||
Dunes | coastal | |
desert | ||
interior | ||
Scrub and Chaparral | coastal bluff scrub | |
coastal scrub | ||
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 | |
valley and foothill grassland | D, < 5% | |
Great Basin grassland | ||
vernal pool | ||
meadow and seep | ||
alkali playa | ||
pebble plain | ||
Bog and Marsh | bog and fen | |
marsh and swamp | ||
Riparian and Bottomland habitat | riparian forest | D, < 5% |
riparian woodland | D, < 5% | |
riparian scrub (incl.desert washes) | ||
Woodland | cismontane woodland | D, < 5% |
piñon and juniper woodland | ||
Sonoran thorn woodland | ||
Forest | broadleaved upland forest | |
North Coast coniferous forest | D, < 5% | |
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
- Central West
- Sierra Nevada East