We have only meagre knowledge of the composition and the functions performed by vegetation in Wisconsin cities. The records of the U.S. Government Land Survey conducted in the 1830s provide information on the presettlement vegetation. Likewise, the notes and letters of settlers and early residents speak of the plants they found here, or brought with them. We know less about the vegetation now growing in our cities

Boehmer, Cecile

Stearns, Forest

English

University of Wisconsin-Milwaukee

University of Wisconsin MilwaukeeUWM Digital CommonsField Station Bulletins UWM Field StationSpring 1981Volunteer urban vegetation of Racine, WisconsinCecile BoehmerUniversity of Wisconsin - MilwaukeeForest StearnsUniversity of Wisconsin-MilwaukeeFollow this and additional works at: https://dc.uwm.edu/fieldstation_bulletinsPart of the Forest Biology Commons, and the Zoology CommonsThis Article is brought to you for free and open access by UWM Digital Commons. It has been accepted for inclusion in Field Station Bulletins by anauthorized administrator of UWM Digital Commons. For more information, please contact open-access@uwm.edu.Recommended CitationBoehmer, C. and F. Stearns. 1981. Volunteer urban vegetation of Racine, Wisconsin. Field Station Bulletin 14(1): 11-14.11VOLUNTEER URBAN VEGETATIONOF RACINE, WISCONSINWe have only meagre knowledge of the composition and the functionsperformed by vegetation in Wisconsin cities. The records of the U.S. Govern-ment Land Survey conducted in the 1830s provide information on the pre-settlement vegetation. Likewise, the notes and letters of settlers and earlyresidents speak of the plants they found here, or brought with them. Weknow less about the vegetation now growing in our cities.Urbanization results in major changes. Hills are lowered, depressionsfilled and hydrologic regimes altered. Forests are cut and fragmented, wet-lands are drained, prairies are plowed and all that remains of the original veg-etation is that set aside in parks or forgotten in small patches along railroads,streams and similar "waste spaces." Urbanization may also follow agricultureas the city expands, again with alteration of the land and vegetation. Someparcels may be used for the same purpose over many years, while elsewherethe land and vegetation are continually disturbed by human activity.This study examined the volunteer, non-native vegetation of urbanRacine. Various sites were examined, some stable, others subject to continu-ous disturbance; plant communities were characterized and compared. Thefindings permit us to draw conclusions as to the nature, composition and lifehistories of the invading species.The Root River floodplain cuts through the heart of Racine, crossingeast through the moraine at a low point. Much of the area is covered by lakeclay deposited while Lake Michigan was at higher post-glacial levels. Theclays are overlain by other deposits of sand and gravel, often mixed withclay and marl. Springs were abundant, particularly along the lakeshore, wherethey emerge above impervious clay layers.The pre-settlement vegetation consisted of prairie and oak openings onthe low dry ridges, wet prairie and other wetland communities along thedrainage ways and in the low depressions (particularly near the lakeshoreon the poorly drained soils). On the upland, northward from the river, mes-ophytic maple forest covered an extensive area.The first permanent settlement at Racine was established by CaptainGilbert Knapp in 1834 (Stone, 1916). He settled at the mouth of the RootRiver which he visualized as an important harbor. Racine prospered and grewfrom a settlement of about 140 acres to a city of 13.3 square miles. The earlysettlers put the clay to good use by developing a brick-making industry.Limestone found near the mouth of the Root River was utilized to manufact-ure lime. About 1842, wheat farming expanded in Racine County; J.1. Caseput together a threshing machine and began manufacturing it. This was thebeginning of Racine industry.12Table 1. Urban habitat typesType Habitat description1. Stabilized lots and parking strips(grass cover 50% or more)2. Fence lines3. Lots along rainroad tracks-stabilized4. Disturbed lots-recent and older(less than 50% grass cover)5. Surfaced areas: asphalt, gravel and brick6. Sidewalks and walls7. Alleys8. Filling station areas9. (Grassland) remnants10. Lake Michigan shorelineTable 2. Comparison of origin and life span of plant species in urbanRacine and Colonial Park and Sanders Park. Colonial Park repre-sents a prairie-grassland type and Sanders Park is a woodland pre-serve.Urban Racine Colonial Park Sanders ParkTotal species 185 114 85Native Species 49.7% 68.4% 91.8%Foreign species 50.3% 31.6% 8.2%Annuals 35.7% 14.1% 5.9%Biennials 5.4% 7.0% 1.2%Perennials 58.9% 78.9% 92.9%Clone formersa 63.3% 46.7% 36.7%apercentages are based on number of perennialsMethodsIn 1973 and 1974, 56 sample sites representing ten different urbanhabitat types were examined (Table 1). Most of the study sites were in theeastern third of Racine, an area bounded by the Chicago Northwestern Rail-road on the west and by Lake Michigan on the east. Two city parks, SaundersPark and Colonial Park, were chosen to represent non-urban conditions.Saunders Park includes 80 acres of mesic hardwood forest and Colonial Parkis a 27-acre area of grassland and prairie. These parks represent the terrestrialplant communities present at the time of settlement.A species list was compiled for each of the 56 sites and for the twoparks. On 36 of the sites, detailed samples were obtained using 25 or more13rectangular quadrats, each 0.1 m 2. These plots provided density and fre-quency information. Species were classed by life span, whether annual, bi-ennial or perennial; by origin, native or foreign; and by their ability to formclones. Ratios between these various characteristics were calculated. Multi-variate analysis was employed to examine the significance of 13 variablesand cluster analysis was used to determine the interrelationships amongthe 36 sites. Ordination methods were utilized to select relationships basedon composition.RESULTSUrban Racine supported at least 185 plant species, Saunders Park 85and Colonial Park 114, a total of 294 species. The two parks proved to bevery different. Of the 185, only 54 urban species were shared with one orboth of the parks (8.6% with Saunders and 26% with Colonial Park). Whenthe park vegetation is compared to the urban vegetation it is evident thatperennials are more prevalent in park vegetation (86% compared to 59%).The urban vegetation also contained a higher percentage of foreign speciesthan did the vegetation in either park. Likewise, clone-forming perennialsare more frequent in the urban sites than in the parks.Both ordination and cluster analyses indicated that most urban standswould fit into three habitat groups instead of 10. These groups are: 1) stabil-ized (or low stress) sites 2) highly disturbed (or high stress) sites and 3) trans-itional sites. In comparing stable with disturbed urban sites, the highlystressed areas show more annuals, 50% compared with 19% for stable sites(Table 3). The increase in proportion of perennials is presumably a resultTable 3. Average species number, density and frequency for perennialsand annuals in high stress and low stress urban habitats.Perennials AnnualsNo. of speciesHigh stress 42% 50%Low stress 70% 19%DensityHigh stress 27% 67%Low stress 80% 8%FrequencyHigh stress 36% 57%Low stress 82% 7%of successional change. Perennials make up 70% of the vegetation in stableurban sites and 42% in heavily disturbed areas. Under the stress caused byfrequent disturbance, (including trampling comparable to overgrazing inrural areas) succession may be reversed. Some plants are in fact adapted tohigh stress areas where trampling is particularly heavy, i.e., in sidewalkcracks, construction sites, etc. Racine shows similar patterns to those Lund(1974) found in Atlanta where he noted that "The continual disturbance ofthe city generally arrests any succession in urban communities." Results14from Racine also indicate that there are more species of foreign origin in theurbanized habitats than elsewhere and that they appear most abundant withinthe older urbanized areas. Some plant species show a haphazard occurrence,presumably resulting from random events of establishment and the passageof time. The ten most prevalent species of the urban environment includedfive perennials, Taraxacum officinale, Plantago major, Medicago lupulina,Trifolium repens and Chicorium intybus, four annuals, Polygonum aviculare,Chenopodium album, Ambrosia artemeslfolia and Polygonum persicaria,and one biennial, Daucus carota.Work on Racine volunteer urban vegetation provides a basis for furtherstudy of plant species adaptation to the frequent and major disturbance often·characteristic of urban habitats. In addition, it should furnish useful infor-mation on the effects of urbanization on wildlife habitat and on variousaspects of the hydrological and biological features.LITERATURE CITEDBoehmer, Cecile M. 1976. A phytosociological study of the voluntary urbanvegetation of Racine, Wisconsin. PhD. Dissertation. University of Wis-consin-Milwaukee. 159pp.Lund, Amme C. 1974. Analysis of urban plant communities of Atlanta,Georgia. PhD. Dissertation. Emory University, Atlanta.Stone, Fanny S., ed. 1916. Racine-Belle City of the Lakes and RacineCounty, Wisconsin. S.]. Clarke Pub!. Co. Chicago.Cecile BoehmerForest StearnsDepartment of BotanyThe University of Wisconsin-Milwaukee

Volunteer urban vegetation of Racine, Wisconsin

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Volunteer urban vegetation of Racine, Wisconsin

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