The highly regulated Green River–AC had the highest density of invasive plant patches (10.1 patches per ha-1), followed by the partially restored Green River–BC (4.4 per ha) and the wild Yampa (3.3 per ha). The species with the highest density of patches along the Green River–AC were tamarisk (Tamarix sp.), Canada thistle (Cirsium arvense), broadleaf pepperwort (Lepidium latifolium), and yellow sweetclover (Melilotus officinalis). On the Green River–BC and Yampa River, tamarisk was the only species with patch densities greater than 1.0 per ha (see chart).
Although patch density was highest on the most-regulated reach, weeds became more widespread on the less-regulated reaches over the two sampling periods. From the first monitoring period (2002–2005) to the next (2010–2011), the total number of patches on the Green River–AC increased by 10%, while the Green–BC and Yampa rivers saw increases of 46% and 43%, respectively. This may be in part because the stable post-dam hydrograph of the Green River–AC had already led to the establishment of vegetation on most of the available post-dam surfaces by 2002–2005, leaving few spaces for invasive species to colonize. In contrast, dynamic fluvial disturbances and flow variability along the Yampa and Green–BC rivers continue to create new spaces and opportunities for spread and persistence of invasive species.
So if riparian areas of more-regulated reaches are more densely populated with invasive plants, but invasives are still spreading on less-regulated reaches, is the invasion process just slower on less-regulated reaches? Or will a wild river continue to maintain lower invasive plant populations than a regulated river? This is where the issue of life-history traits bears examination. Using large, international datasets, Catford and Jansson (2014) indicated that successful non-native invaders of riparian zones generally have high seed availability and dispersal potential, often occupy high, dry locations within the riparian zone, and are adapted to or tolerant of flood disturbance—all of which may reduce competition with native plants.
The life-history traits of many of the invasive, non-native herb species in this study are consistent with these findings. Because many of them are associated with human activities that are common on river floodplains, such as grazing and agriculture (AKEPIC 2015), riparian zones are subject to continual inputs of propagules. These species are likely to continue to invade and persist to some degree in riparian settings regionally, regardless of the degree of flow regulation. Flow regulation alone is likely not the only factor driving riparian invasion. Future monitoring and management of invasive species in riparian ecosystems would benefit by including knowledge of key life-history traits, hydrological variables, and site-scale distribution along physical environmental gradients (Mortenson and Weisberg 2010; Catford and Jansson 2014).
Material in this brief was summarized from Perkins, D. W., M. L. Scott, and T. Naumann. 2015. Abundance of invasive, non-native riparian herbs in relation to river regulation. River Research and Applications.
AKEPIC 2015. Alaska Exotic Plant Information Clearinghouse database. Alaska Natural Heritage Program, University of Alaska, Anchorage.
Catford, J. A., B. J. Downes, C. J. Gippel, and P. A. Vesk. 2011. Flow regulation reduces native plant cover and facilitates exotic invasion in riparian wetlands. Journal of Applied Ecology 48:432–442.
Catford, J. A., and R. Jansson. 2014. Drowned, buried and carried away: Effects of plant traits on the distribution of native and alien species in riparian ecosystems. New Phytologist 204:19–36.
Mortenson S. G., and P. J. Weisberg. 2010. Does river regulation increase the dominance of invasive woody species in riparian landscapes? Global Ecology Biogeography 19:562–574.
Download a pdf of this brief