Abstract
Located in Oconto County, Wisconsin, Oconto Marsh #2 is a Great Lakes Coastal Wetland Monitoring Program study site that borders the shoreline of Lake Michigan. Plant communities were characterized at Oconto Marsh #2 along three transects in 2011, 2016, 2017 and 2021, a period when Lake Michigan water levels increased by two meters. Transects were placed to intersect with three vegetation zones: submergent, emergent, and wet meadow. Here, we report on physical landscape changes and the vegetation composition changes that occurred from 2011 to 2021. From satellite imagery interpretation, we show approximately 61,000 m2 of what was emergent and wet meadow vegetation in 2011, transitioned into a submerged aquatic community in 2021. High energy wave action penetrating farther landward, a consequence of higher water levels, is likely most responsible for causing these changes. Plant species richness was lowest in 2011 (32 species) and ranged from 52 to 56 taxa in later years. Using multivariate ordination and PERMANOVA, we show plant composition in 2011 was different from 2016, 2017, and 2021. While invasive Phragmites australis was treated with herbicide in 2014, disturbance from progressively increasing water levels has facilitated considerable changes in plant composition and wetland zone extents since monitoring began. Despite successful treatment of P. australis, encounters with more non-native species while sampling farther landward in later years has caused site-wide declines in multiple metrics of floristic quality. Of critical importance, in 2021, we discovered invasive Hydrocharis morus-ranae at the site, the first documentation in the state of Wisconsin.
This is a preview of subscription content, access via your institution.

Source: National Oceanic and Atmospheric Administration: https://tidesandcurrents.noaa.gov/). b Aerial photos of the Oconto Marsh #2 and sampling points along research transects for 2011, c 2016, and d 2018. Wet meadow zone: blue points; Emergent zone: pink points, Submergent zone: white points. Yellow circles at the transect terminal ends represent the original endpoints established in 2011. County Road Y is shown in yellow. Satellite imagery from Google Earth (years 2013, 2015, and 2018)





Data availability
Data will be made available upon request to the corresponding author.
Code availability
Not applicable.
References
Albert DA, Minc LD (2004) Plants as regional indicators of Great Lakes coastal wetland health. Aquat Ecosyst Health Manage 7:233–247
Albert DA, Wilcox DA, Ingram JW, Thompson TA (2005) Hydrogeomorphic classification for Great Lakes coastal wetlands. J Great Lakes Res 31:129–146. https://doi.org/10.1016/S0380-1330(05)70294-X
Bourgeau-Chavez LL, Graham J, Battaglia MJ, White L, Klassen J, VanderBilt DL, Poley AF, Pelletier K, Brisco B, Huberty B (2021) Great Lakes Remote Sensing ESRI Storymap, High resolution monitoring of coastal Great Lakes wetlands in 4D. https://mtu.maps.arcgis.com/apps/MapSeries/index.html?appid=2d06583e97844ea892413e2290cbe885
Bourdaghs M, Johnston CA, Regal RR (2006) Properties and performance of the Floristic Quality Index in Great Lakes coastal wetlands. Wetlands 26:718–735. https://doi.org/10.1672/0277-5212(2006)26[718:PAPOTF]2.0.CO;2
Catling PM, Mitrow G, Haber E, Posluszny U, Charlton WA (2003) The biology of Canadian weeds. 124. Hydrocharis morsus-ranae L. Can J Plant Sci 83:1001–1016. https://doi.org/10.4141/p02-033
Catling PM, Spicer K, Lefkovitch L (1988) Effects of the introduced floating vascular aquatic Hydrocharis morsus-ranae (Hydrocharitaceae), on some north American aquatic macrophytes. Naturaliste Can 115:131–137
DeBoer LS, Rothrock PE, Reber RT, Namestnki SA (2011) The use of floristic quality assessment as a tool for monitoring wetland mitigations in Michigan. Mich Bot 50:146–165
Dybiec JM, Albert DA, Danz NP, Wilcox DA, Uzarski DG (2020) Development of a preliminary vegetation-based indicator of ecosystem health for coastal wetlands of the Laurentian Great Lakes. Ecol Ind 119:106768. https://doi.org/10.1016/j.ecolind.2020.106768
Freyman WA, Masters LA, Packard S (2016) The universal Floristic Quality Assessment (FQA) calculator: an online tool for ecological assessment and monitoring. Methods Ecol Evol 7:380–383. https://doi.org/10.1111/2041-210X.12491
Geddes P, Murphy L, Astudillo-Scalia Y, Blasini D (2021) Microsatellite markers reveal unprecedented high frequencies of hybridization among Typha species in the Midwestern US. Wetlands. https://doi.org/10.1007/s13157-021-01429-2
Hartsock JA, House M, Clark MG, Vitt DH (2021) A comparison of plant communities and water chemistry at Sandhill Wetland to natural Albertan peatlands and marshes. Ecol Eng 169:106313. https://doi.org/10.1016/j.ecoleng.2021.106313
Hartsock JA, Schwarting RJ, Beaster K, Danz NP (2022) Coastal wetland plant community responses to record-high Lake Superior water levels: An Allouez Bay case study. Journal of Great Lakes Research (in press)
Herman KD, Masters LA, Penskar MR, Reznicek AA, Wilhelm GS, Brodowicz WW (1997) Floristic quality assessment: development and application in the state of Michigan (USA). Nat Areas J 17:265–279
Hohman TR, Tozer D, Gnass Giese EE, Howe RW (2021) Influence of lake levels on water extent, interspersion, and marsh birds in Great Lakes coastal wetlands. J Great Lakes Res 47:534–545. https://doi.org/10.1016/j.jglr.2021.01.006
Johnston CA, Brown TN (2013) Water chemistry distinguishes wetland plant communities of the Great Lakes coast. Aquat Bot 104:111–120. https://doi.org/10.1016/j.aquabot.2012.08.005
Kottek M, Grieser J, Beck C, Rudolf C, Rubel F (2006) World map of the Köppen-Geiger climate classification updated. Meteorol Z 15:259–263
Kozlowski TT (ed) (1984) Flooding and plant growth. Academic Press, Orlando, Florida
Lishawa SC, Lawrence BA, Albert DA, Larkin DJ, Tuchman NC (2019) Invasive species removal increases species and phylogenetic diversity of wetland plant communities. Ecol Evol 9:6231–6244. https://doi.org/10.1002/ece3.5188
McCune B, Mefford MJ (2015) PC-ORD, multivariate analysis of ecological data. Version 7.01. Glenden Beach, OR: MjM software
Medley L, Scozzafava M (2009) Moving toward a national floristic quality assessment: considerations for the EPA National Wetland Condition Assessment National Wetlands Newsletter 31:6–9
Monks AM, Lishawa SC, Wellons KC, Albert DA, Mudrzynski BM, Wilcox DA (2019) European frogbit (Hydrocharis morsus-ranae) invasion facilitated by non-native cattails (Typha) in the Laurentian Great Lakes. Journal of Great Lakes Research
MRCC (2021) Climate summary for stations USC00476208 – Oconto 4 W, WI and USW00014898 – Green Bay A S INTL AP, WI. https://mrcc.illinois.edu/mw_climate/climateSummaries/climSumm.jsp. Accessed 25 Oct 2021
Prince HH, Padding PI, Knapton RW (1992) Waterfowl use of the Laurentian Great Lakes. J Great Lakes Res 18:673–699
Robichaud CD, Rooney RC (2021) Effective suppression of established invasive Phragmites australis leads to secondary invasion in a coastal marsh. Invas Plant Sci Manag 14(9–19):11
Saltonstall K (2002) Cryptic invasion by a non-native genotype of the common reed, Phragmites australis, into North America. Proc Natl Acad Sci 99:2445–2449. https://doi.org/10.1073/pnas.032477999
Sculthorpe CD (1967) The biology of aquatic vascular plants (reprinted in 1985). Edward Arnold, London
Smith IM, Fiorino GE, Grabas GP, Wilcox DA (2021) Wetland vegetation response to record-high Lake Ontario water levels. J Great Lakes Res 47:160–167. https://doi.org/10.1016/j.jglr.2020.10.013
Spence DHN (1982) The zonation of plants in freshwater lakes. Adv Ecol Res 12:37–125
Spyreas G (2016) Scale and sampling effects on floristic quality. PLoS ONE 11:e0160693–e0160693. https://doi.org/10.1371/journal.pone.0160693
Stanley KE, Murphy PG, Prince HH, Burton TM (2005) Long-term ecological consequences of anthropogenic disturbance on Saginaw Bay coastal wet meadow vegetation. J Great Lakes Res 31:147–159
Swink F, Wilhelm GS (1979) Plants of the Chicago region, 3rd ed. Morton Arboretum, Lisle, IL. 922 pp.
Trebitz AS, Taylor DL (2007) Exotic and invasive aquatic plants in great lakes coastal wetlands: distribution and relation to watershed land use and plant richness and cover. J Great Lakes Res 33:705–721. https://doi.org/10.3394/0380-1330(2007)33[705:EAIAPI]2.0.CO;2
Uzarski DG et al (2017) Standardized measures of coastal wetland condition: Implementation at a Laurentian Great Lakes basin-wide scale. Wetlands 37:15–32. https://doi.org/10.1007/s13157-016-0835-7
Wellons KC (2018) Ecophenology and control of European frogbit in a hybrid cattail marsh of the St. Marys River, Michigan. Master’s thesis Oregon State University. https://ir.library.oregonstate.edu/concern/graduate_thesis_or_dissertations/7w62ff52m
Wasko JD, McGonigle TP, Goldsborough LG, Wrubleski DA, Badiou PH, Armstrong LM (2022) Use of shoot dimensions and microscopic analysis of leaves to distinguish Typha latifolia, Typha angustifolia, and their invasive hybrid Typha x glauca. Wetlands Ecol Management 30:19–33. https://doi.org/10.1007/s11273-021-09836-2
Zedler JB, Kercher S (2004) Causes and consequences of invasive plants in wetlands: opportunities, opportunists, and outcomes. Crit Rev Plant Sci 23:431–452. https://doi.org/10.1080/07352680490514673
Acknowledgements
We thank two anonymous reviewers for their contributions in improving this paper. We thank Dr. Dennis Albert and Courtney Fung for reading the manuscript and providing helpful comments. We thank past field sampling crew members M. Jahnke, M. Hogfeldt, N. Dahlberg, and J. Rutherford. This work was funded by the Great Lakes Restoration Initiative as provided by the Great Lakes National Program Office of the United States Environmental Protection Agency, grant numbers GL-00E00612-0, 00E01567 and 00E02956. Although the research described in this work has been funded by the USEPA, it has not been subjected to the agency's required peer and policy review and therefore does not necessarily reflect the views of the agency and no official endorsement should be inferred.
Funding
Funding for this work was provided by the Great Lakes National Program Office under the United States Environmental Protection Agency, grant numbers GL-00E00612-0, 00E01567, and 00E02956 as part of the US federal government’s Great Lakes Restoration Initiative.
Author information
Authors and Affiliations
Contributions
RR—Field work, wrote the manuscript, organized the data, created figures and tables. JH—Field work, created figures. ND—Principal investigator, project conceptualization, assisted writing the manuscript.
Corresponding author
Ethics declarations
Conflict of interest
The author declares that they have no conflict of interest.
Ethical approval
Not applicable.
Consent to participate
Not applicable.
Consent for publication
All authors give consent for the manuscript to be published in its current form.
Additional information
Publisher's Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary Information
Below is the link to the electronic supplementary material.
Rights and permissions
About this article
Cite this article
Rutherford, R., Hartsock, J.A. & Danz, N.P. Physical and plant community changes at a Lake Michigan coastal marsh related to a two-meter increase in lake level. Wetlands Ecol Manage 30, 547–560 (2022). https://doi.org/10.1007/s11273-022-09879-z
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s11273-022-09879-z
Keywords
- Great lakes
- Lake Michigan
- Coastal Wetlands
- Marsh
- Plant communities
- European frogbit
- Phragmites