please consult the experts…

please consult the experts in these matters, not just hearsay and public opinion (or political opinions for that matter) -_-
I was unable to attach a PDF so here are Prof. Gail Fraser's comments on the proposed cormorant hunt:

Comments submitted on Proposed double-crested cormorant hunt in Ontario,
EBR Registry Number: 013-4124
Gail Fraser, Associate Professor, Faculty of Environmental Studies, York
University
Background. I study and teach the biology and management of colonial nesting
waterbirds. Both my MSc and PhD were on colonial nesting waterbirds. Since
2006 I have undertaken research on double-crested cormorants (hereinafter
cormorants) and participated in The Toronto and Region Conservation Authority’s
Cormorant Working Group. I have an ongoing long-term monitoring project (10
yrs) following breeding chronology and productivity cormorants and blackcrowned
night-herons. My students and I have also undertaken other cormorantrelated
research projects which fall outside of the monitoring goals. This research
has thus far resulted in six peer-reviewed publications specific to cormorants and
cormorant management (McDonald et al. 2018, Gupta et al. 2017, McRae et al.
2017, Andrews et al. 2012, Taylor et al. 2012, Taylor and Fraser 2011).
Introduction. In this document I respond to the proposal for a cormorant hunt in
Ontario. I structure my comments following the Policy Proposal Notice:
Description of the Policy, the proposed hunting regulations, the Purpose of the
Policy and Regulatory Impact Statement. Items from the proposal will be italics,
my comments will follow in normal text.
Description of Policy.
There continues to be concerns expressed by some groups (commercial fishing
industry, property owners) and individuals that cormorants have been detrimental
to fish populations, island forest habitats, other species and aesthetics.
I am opposed to this proposal and provide rationale for my position below.
This proposal originates from the OMNRF and as such the justifications
provided for a cormorant hunt should be science-based. The generic statements
on double-crested cormorants without data to back such statements are a
problem. The OMNRF should have a full and detailed rationale to provide
justification for this proposal, as well as population modelling exercises,
population level targets to support the extreme daily bag numbers being
proposed, exactly how the cormorant population will be monitored to determine
effects of a hunt and an evaluation of the negative impacts on non-target
species.
1. Detrimental to fish populations. The science behind determining whether a
cormorant population has a negative effect on a particular fish population is
complex (Wires et al. 2003). There are factors that could negatively impact
the abundance of a particular fish population: human predation, predatory
fish (multiple species), predation by other waterbirds (e.g., red-breasted
merganser; Bur et al. 2008), competition from other prey which would
include multiple species, abiotic considerations (e.g., water temperature) etc.
Thus, rigorous scientific studies are required for each fish population
consumed by cormorants (Wires et al. 2003; see also Dorr et al. 2014 for a
summary of cormorant fish predation).
As one of the presumed intentions of this proposal is to increase fish
abundance by reducing cormorant predation, additional factors which
influence fish populations should be considered (see Wires et al. 2003). For
example, predicted changes in the distribution and abundance of walleye due
to climate change (see Van Zuiden et al. 2016); and how changes in lake ice
will modify aquatic food webs (Ontario Biodiversity Council 2015) should
be considered.
2. Island habitats. Cormorants nest in high densities (Dorr et al. 2014). Where
they nest in trees they will cause the mortality of trees in 10-15 years (e.g.,
Lemmon et al. 1994; Herbert et al. 2014) which is a natural ecological
process. Cormorants do not occupy all available island habitat; they have
only occupied 3% of the U.S. Great Lakes islands over a 30-year period
(Wires and Cuthbert 2010).
If particular islands or forest patches that host at-risk species are being
significantly modified by cormorants, local, small scale management such as
deterrence and culling (e.g., Middle Island, Point Peele National Park) may
be appropriate1. Non-lethal management, deterrence and knocking down
1 Though in the case of Middle Island, I would argue a cull is not warranted as the Carolinian
species are at-risk because they are at the northern edge of their range (see Brown et al. 1998 for
concepts on species range and abundance).
nests, should be used first to disperse them (McDonald et al. 2018). For
roosting cormorants, a tethered raptor has successfully displaced birds
(Quinn et al. 2012).
Aesthetics are presumably an additional factor for this section. People
dislike the change of a forested island to a non-forested island. Yet,
ecological processes involve change. Cormorants are a native species to
Ontario and this is what they do. On a far larger scale, humans are
significantly modifying the landscape in Ontario. For example, in Ontario
forest cover the mixedwood plains ecoregion is declining (Ontario
Biodiversity Council 2015); and agriculture is a primary a driver of species
endangerment in this ecoregion (Kerr and Cihlar 2004).
3. Other species. In general, competition within and among species is a part of
evolution and proposing a provincial wide cull because one out-competes
another is a disproportionate response and not necessary.
Cormorants nest with other species both in trees and on the ground. Treenesting
cormorants can nest among great blue herons, black-crowned nightherons,
and great egrets (see Rush et al. 2015 and references therein).
Caspian terns and ring-billed and herring gulls can co-occur with groundnesting
cormorants. This means there are a considerable number of species
which could be disturbed from humans on or near colonies; and hunting
activities will be detrimental to all birds nesting nearby (Carney and
Sydeman 1999). Disturbance to non-target birds would presumably violate
the Migratory Bird Convention Act.
I will include comments on the positive impact cormorants have for bald
eagles. Bald eagles were de-listed from the Endangered Species listing in the
U.S. and their population is increasing in Ontario, though they are still listed
a species of special concern in Canada (Armstrong 2014; Environment and
Climate Change Canada 2017). Bald eagles on the Atlantic coast are
negatively impacting seabird colonies by preying on adults and chicks
(Hipfner et al. 2012) and farmers’ chickens (Williams 2017). In Minnesota
cormorant remains were found in 40% of bald eagle nests (Windels et al.
2016). Ecologists predict a top-down effect of bald eagles on waterbird
populations (Hipfner et al. 2012); bald eagles can take adult cormorants as
well as juveniles and disrupt nesting colonies which can result in a site
abandonment (Cairns et al. 1998; Armstrong 2014; Windels et al. 2016,).
Based on other locations, it is likely that cormorants will provide a
significant source of prey for bald eagles in Ontario in the near future and
may assist in achieving the population recovery goal for the eagles identified
by the OMNRF (Armstrong 2014). Bald eagle predation should be
incorporated into a model on what may suppress the cormorant population in
Ontario. In addition, the potential economic impact to free-range chicken
farmers in reducing an abundant prey (cormorants) for bald eagles should
also be under consideration.
To respond to these concerns, the Ministry is proposing to create a hunting season
for double-crested cormorants in Ontario. This new population management tool
would allow persons who hold a small game licence to hunt these birds.
List the double-crested cormorant as a “Game Bird”. Hunters would be required
to have an outdoors card and small game licence to hunt double-crested
cormorants, similar to other species of game birds.
Create an open hunting season for double-crested cormorant from March 15 to
December 31 each year across the province. Create an exemption allowing small
game licences to be valid for double-crested cormorant hunting in central and
northern Ontario from June 16 to August 31 each year….. Monitoring of
cormorants will allow the Ministry to assess the impacts of the hunting season and
to adjust cormorant hunting regulations if necessary to address any concerns
about population sustainability.
Unlike ducks and mergansers, cormorants have altricial young where both
members of a pair are required for nest success. The killing of either a male
or a female during the breeding season will result in their chicks starving to
death even if the other parent is present. How will the sustainability of this
cull be assessed in this regard? Monitoring of the cormorant population will
be done presumably via nest counts, but this approach does not assess
reproductive success. Where strong rationale and evidence is provided, a
controlled, local cull by OMNRF would avoid this situation. At Point Peele
National Park, adult cormorants are shot at the nest site early in the nesting
season when no chicks are present, thus permitting a reduction in nest
density but avoiding unnecessary suffering and mortality of young (e.g.,
Dobbie and Kehoe 2012).
Allow hunting from a stationary motorboat.
There is no mention of restricting hunting on or near colonies. Hunting on or
near colonies would almost certainly disturb ground-nesting colonies, as
well as disturb non-target, co-nesting species. Cormorants will disperse to
other locations; including new tree sites where available. A study using
marked cormorants showed that the management actions of complete nesting
failure resulted in the dispersal of adults to sites without management (Duerr
et al. 2007). The dispersing adults established 10 new colonies, and in some
cases, moved up to 100 km away (Duerr et al. 2007)2. Disturbance to
nesting sites may also have the indirect effect of increased predation on
nests, thus lowering productivity even further and causing more dispersal
(Carney and Sydeman 1999; Duerr et al. 2007).
There is, presumably, also a significant risk to recreational boaters given that
the proposed hunting season is throughout the summer months. When
queried, the Toronto Marine Police did not know where the municipal
boundary was on Lake Ontario with respect to hunting. They confirmed that
at a minimum fire arm discharge would not be permitted within the harbor.
Municipal boundary lines need delineation for all coastal cities and towns to
ensure public safety.
The Fish and Wildlife Conservation Act currently prohibits anyone who kills game
wildlife (including game birds), or who possesses game wildlife killed by hunting,
from allowing that meat to spoil. Via this posting, the Ministry is also consulting
on a proposal to amend the Fish and Wildlife Conservation Act to add provisions
so hunters could allow cormorant to spoil. This proposal would add provisions to
the Act, so that persons who lawfully hunt (or possess) cormorants could be
exempt from this requirement and would be subject to conditions that require the
person to retrieve and dispose of the carcass. Should this proposal proceed, it may
be accompanied by regulations to implement the exemption and requirements.
2 While there was a significant banding effort for cormorants in the early 2000s in Ontario and
some banded birds remain, there is no effort in re-sighting marked birds before and after the
hunting would occur, to establish residency and change of residency.
A controlled, focused management action by the OMNRF is preferred over a
public hunt because appropriate steps would be taken to consult the public: it
would be a targeted
local action; data (i.e., date, location, the number of birds shot) would be
collected; a target of the number of birds to be killed would be articulated;
disposal would properly occur; and other data could be gathered from the
killed birds (e.g., Coleman et al. 2012).
A public hunt may disperse cormorants into new areas creating more
conflicts – potentially moving ground-nesting birds to new tree or ground
habitat and reduce prey for bald eagles.
A blanket open season on double-crested cormorants is not warranted and its
impacts would be difficult to monitor.
The change to the Fish and Wildlife Act to permit game wastage is
unprecedented, a serious change to the Act and completely unethical.
To accompany the proposed hunting seasons, the Ministry will implement a
cormorant monitoring program to assess population status and trends. Monitoring
of cormorants will allow the Ministry to assess the impacts of the hunting season
and to adjust cormorant hunting regulations if necessary to address any concerns
about population sustainability.
Cormorants are a species native to Ontario (Dorr et al. 2014, McIlwraith
1894). A significant amount of financial resources was invested in creating a
healthier environment which allowed the recovery of this species; their
abundance is a conservation success story (Weseloh and Collier 1995).
Should this proposal be approved, specific targets should be articulated for
the cormorant population in Ontario. To avoid the species becoming
endangered again, these targets should be set prior to a hunt and their
populations carefully monitored. Annual monitoring data should be released
to the public on a timely basis for comment.
This proposed hunt places other aquatic waterbirds species at risk,
particularly ones that nest with cormorants (herons, egrets and gulls and
terns). Disturbance from hunting on non-target birds should not be
underestimated; for example, it can displace birds from foraging areas and
disrupt breeding (Masden and Fox 1995; Cairns et al. 1998). Should this
proposal proceed, how will the impact on other waterbird species be
monitored?
Since the proposal is for all of Ontario, enforcement and monitoring will be
minimal and that alone should be the basis for a rejection of this proposal.
Literature Cited
Andrews, D., G.S. Fraser and D.V. Weseloh. 2012. Double-crested cormorant
foraging ecology at a large colony in southern Ontario: Analyses of chick diet,
feeding rates and foraging directions. Waterbirds 35(sp1): 82-90.
Armstrong, E.R. 2014. Management Plan for the Bald Eagle (Haliaeetus
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Brown, J., T.E. Brown and M. Lomolino 1998. Biogeography, 2nd edition. Sinauer
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