Sensitivity of invasion speed to dispersal and demography: an application of spreading speed theory to the green crab invasion on the northwest Atlantic coast

2015 ◽  
Vol 541 ◽  
pp. 135-150 ◽  
Author(s):  
A Gharouni ◽  
MA Barbeau ◽  
A Locke ◽  
L Wang ◽  
J Watmough
Mathematics ◽  
2019 ◽  
Vol 7 (9) ◽  
pp. 795 ◽  
Author(s):  
Aled Morris ◽  
Luca Börger ◽  
Elaine Crooks

We model the growth, dispersal and mutation of two phenotypes of a species using reaction–diffusion equations, focusing on the biologically realistic case of small mutation rates. Having verified that the addition of a small linear mutation term to a Lotka–Volterra system limits it to only two steady states in the case of weak competition, an unstable extinction state and a stable coexistence state, we exploit the fact that the spreading speed of the system is known to be linearly determinate to show that the spreading speed is a nonincreasing function of the mutation rate, so that greater mixing between phenotypes leads to slower propagation. We also find the ratio at which the phenotypes occur at the leading edge in the limit of vanishing mutation.


Heredity ◽  
2017 ◽  
Vol 119 (3) ◽  
pp. 154-165 ◽  
Author(s):  
N W Jeffery ◽  
C DiBacco ◽  
B F Wringe ◽  
R R E Stanley ◽  
L C Hamilton ◽  
...  

2017 ◽  
Vol 7 (8) ◽  
pp. 2513-2524 ◽  
Author(s):  
Nicholas W. Jeffery ◽  
Claudio DiBacco ◽  
Mallory Van Wyngaarden ◽  
Lorraine C. Hamilton ◽  
Ryan R. E. Stanley ◽  
...  

Author(s):  
Beth Cameron ◽  
Anna Metaxas

Patterns in larval supply and recruitment of the invasive European green crab, Carcinus maenas, were examined at two sites in Nova Scotia, Canada: a typical Atlantic coastal site with high salinity (∼33) and strong tidal signal (Terence Bay); and a microtidal site in the Bras d'Or Lakes, where surface salinity fluctuated from 0 to 23 (Benacadie Pond). Abundance of all life history stages (zoeae, megalopae, juveniles and ovigerous females) was sampled approximately biweekly at each site from June 2001 to June 2002. The reproductive season, based on the presence of ovigerous females, is ∼5 months (June to October) at both sites. Zoeae-I were collected from June to July 2001 and in June 2002 at Terence Bay, and from June to August 2001 at Benacadie Pond. We did not collect later zoeal stages at either site. Megalopae were collected from September to October 2001 at Terence Bay, and from August to September 2001 at Benacadie Pond. Juveniles 1–6 mm carapace width (CW) were present throughout the summer at Terence Bay, and only in autumn at Benacadie. Juveniles 6–12 and 12–27 mm CW were present throughout the summer and autumn at both sites. At Terence Bay, densities of 1–6 and 12–27 mm CW juveniles did not vary among intertidal zones. In contrast, the 6–12 mm CW size-class appeared to move higher in the intertidal through the season, possibly due to effects of predation.


2015 ◽  
Vol 532 ◽  
pp. 153-159 ◽  
Author(s):  
LM Williams ◽  
CL Nivison ◽  
WG Ambrose ◽  
R Dobbin ◽  
V Locke WL

2022 ◽  
Author(s):  
Nicholas Josiah Ens ◽  
Bronwyn Harvey ◽  
Morgan M. Davies ◽  
Hanna M. Thomson ◽  
Keegan J. Meyers ◽  
...  

The European green crab (Carcinus maenas), native to northwestern Europe and Africa, is among the top 100 most damaging invasive species globally. In some regions, including the Atlantic coast of North America, C. maenas has caused long-term degradation of eelgrass habitats and bivalve, crab, and finfish populations, while areas are near the beginning of the invasion cycle. Due to high persistence and reproductive potential of C. maenas populations, most local and regional mitigation efforts no longer strive for extirpation and instead focus on population control. Long-term monitoring and rapid response protocols can facilitate early detection of introductions that is critical to inform management decisions related to green crab control or extirpation. Once C. maenas are detected, local area managers will need to decide on management actions, including whether and what green crab control measures will be implemented, if local invasion might be prevented or extirpated, and if population reduction to achieve functional eradication is achievable. Due to the immense operational demands likely required to extirpate C. maenas populations, combined with limited resources for monitoring and removal, it is unlikely that any single government, conservation and/or academic organization would be positioned to adequately control or extirpate populations in local areas, highlighting the importance of collaborative efforts. Community-based monitoring, and emerging methods such as environmental DNA (eDNA), may help expand the spatial and temporal extent of monitoring, facilitating early detection and removal of C. maenas. While several C. maenas removal programs have succeeded in reducing their populations, to our knowledge, no program has yet successfully extirpated the invader; and the cost of any such program would likely be immense and unsustainable over the long-term. An alternative approach is functional eradication, whereby C. maenas populations are reduced below threshold levels such that ecosystem impacts are minimized. Less funding and effort would likely be required to achieve and maintain functional eradication compared to extirpation. In either case, continual control efforts will be required as C. maenas populations can quickly increase from low densities and larval re-introductions.


Sign in / Sign up

Export Citation Format

Share Document