Dredging
Description: Starry stonewort is a non-native species of large algae in the Characeae family. It has whorls of 4-6 long branchlets. It is more robust than most members of its family, and can grow to over two meters tall. Anchored by colorless filaments (rhizoids) that contain up to several dozen 4-5mm, star-shaped bulbils, starry stonewort typically grows in marl sediments of alkaline lakes, up to 9 meters deep. Orange, male reproductive structures are located in the axils of the upper branchlets. Starry stonewort typically dies back to the sediments in the fall, but may persist during mild winters. Interestingly, starry stonewort is listed as an endangered species in the United Kingdom.
North American Distribution: Michigan, northern Indiana, and the northeastern United States. Recently found in Wisconsin and Minnesota.
Dispersal Vectors: Starry stonewort is native to Europe and western Asia. It was probably introduced to the Great Lakes via ballast water carried in trans-oceanic ships. Fragments of starry stonewort can be spread between lakes by boats, trailers, and anchors holding sediments. Local dispersal occurs by bulbils or fragments being transported by water currents or boats within the lake. Since only male starry stonewort exists in the U.S., no viable "seeds" are produced.
Ecological Impacts: By forming dense mats of vegetation, starry stonewort can reduce the diversity of aquatic plants in a lake. It can also impede movement of fish and other animals, and may impact spawning activity of some fishes. Mats growing to the surface can reduce water flow and make recreational activities difficult.
Control Options: Manual removal of starry stonewort is possible, but difficult, and may be impractical on a large scale. Abundant bulbils on the rhizoids can dislodge if disturbed, and will sprout new individuals. Manual removal efforts must emphasize careful removal of these bulbils.
Some chemical herbicides and algaecides have been effective at reducing starry stonewort. Herbicide applications may be less effective on tall stands of starry stonewort, as the chemical is quickly absorbed into the upper parts of the algae, leaving the lower parts unharmed. Most states require
chemical use permits for any herbicide/algaecide treatments in standing water or wetland situations.
An effective biological control agent is not known at this time.
Additional Information:
Brown, W.S. 2014. Defining trophic conditions that facilitate the establishment of an invasive plant: Nitellopsis obtusa. Master's thesis. University of Illinois - Urbana Champaign.
Photo credit: Paul Skawinski
This Quick Guide is part of a series on aquatic invasive species, and may be reproduced for educational purposes. Visit us at www.uwsp.edu/cnr/uwexlakes/clmn or www.goldensandsrcd.org/our-work/water to download this series of handouts. Developed by Golden Sands Resource Conservation & Development Council, Inc. as part of an aquatic invasive species education program, supported by a grant from the Wisconsin Department of Natural Resources. Maintained and updated by the Wisconsin Citizen Lake Monitoring Network.