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8/9/2019 Trends Ecol Evol (Amst) 2015 Dall SR
http://slidepdf.com/reader/full/trends-ecol-evol-amst-2015-dall-sr 1/7
Genes as cues: phenotypic integrationof genetic and epigenetic information
from a Darwinian perspectiveSasha R.X. Dall1, John M. McNamara1,2, and Olof Leimar3
1Centre for Ecology and Conservation, Biosciences, College of Life and Environmental Sciences, University of Exeter,
Penryn Campus, Tremough, Penryn TR10 9EZ, UK2School
of
Mathematics,
University
of
Bristol,
University
Walk,
Bristol
BS8
1TW,
UK3Department of Zoology, Stockholm University, SE-106 91 Stockholm, Sweden
The
development
of
multicellular
organisms
involves
a
delicate interplay between genetic and environmental
influences. It is often useful to think of developmental
systems as integrating available sources of informationabout current conditions to produce organisms. Genes
and inherited physiology provide cues, as does the state
of the environment during development. The integration
systems
themselves
are
under
genetic
control
and
sub-
ject to Darwinian selection, so we expect them to evolve
to produce organisms that fit well with current ecologi-
cal
(including
social)
conditions.
We
argue
for
the
scien-
tific value of this explicitly informational perspective by
providing detailed examples of how it can elucidate
taxonomically
diverse
phenomena.
We
also
present
a
general framework for linking genetic and phenotypic
variation from an informational perspective. This appli-
cation
of
Darwinian
logic
at
the
organismal
level
canelucidate genetic influences on phenotypic variation in
novel and counterintuitive ways.
Development
and
cue
integration
The
textbook
depiction
of
genes
as
‘recipes’
that
determine
organismal phenotypes is increasingly difficult to sustain
in the
modern
biological
sciences
[1,2].
Phenotypic
plastic-
ity
–
the
ability
of
a
genotype
to
produce
distinct
pheno-
types as a result of nongenetic influences during
development
–
may
be
ubiquitous
in
multicellular
organ-
isms [1,3]. Such nongenetic influences (here referred to
collectively as epigenetic) can include environmental cues
and ‘parental effects’ (including vertical cultural inheri-
tance
and
DNA-methylation
patterns)
[1,3,4], which
often
reflect
parental
experience
of
the
local
selective
environ-
ment [5]. However, it is underappreciated that genes
themselves
can
also
act
as
cues
of
the
current
environment
[5–9]. If
there
is
restricted
gene
flow
among
local
environ-
ments with differential fitness effects of alleles in different
environments,
allele
frequencies
will
vary
spatially
[10]. Therefore,
an
individual’s
genotype
will
statistically
contain
information
about
(correlate
with)
local
environ-
mental conditions and can be regarded as a genetic cue. In
effect, genes at polymorphic loci provide information thatthe phenotypic states they trigger have had local success
[5–7,10]. Furthermore,
at
the
level
of
developmental
mech-
anisms, there is considerable overlap in how environmen-
tal
cues
and
genetic
variation
determine
phenotypes
[1,11].
Here
we
aim
to
provide
a
general
framework
for
think-
ing about how potential cues are integrated during devel-
opment
to
maximise
the
fit
of
the
phenotype
to
current
ecological
(including
social)
conditions.
Such
integration
will be favoured by Darwinian selection if the cue integra-
tion
system
is
itself
under
genetic
control
[7].
For
instance,
a polymorphic ‘genetic cue’ locus might influence the hor-
monal
regulation
of
phenotypes,
either
by
encoding
tran-
scription
factors
that
modulate
gene
expression
at
otherloci [12] and influence circulating hormone levels or by
influencing
hormone
receptors
[11,13]. Similarly,
develop-
ing phenotypes can be modulated by epigenetic parental
effects
(e.g.,
genomic
imprints,
maternal
effects)
and
the
state
of
the
local
environment.
By
influencing
transcription
in target tissues, hormone receptors can ‘integrate’ these
inputs
[14,15], thereby
guiding
phenotypic
development
[14]. In
summary,
evolutionary
change
of
developmental
systems
occurs
via
selection
on
modifier
loci
(e.g.,
that
influence
tissue-specific
hormone
receptor
densities),
fi-
ne-tuning responses to developmental cues. Modifiers
might
often
be
regulatory
genes.
Adaptive
cue-integration
systems
of
the
sort
outlinedabove will take any available sources of information (epi-
genetic
and
genetic)
into
account
in
determining
pheno-
types. Our framework predicts that the relative weights
put on
each
source
of
information
should
depend
on
envi-
ronmental
characteristics,
such
as
its
temporal
stability,
and on cue accuracies. If correlations among allele frequen-
cies
at
a
cue
locus
and
local
ecological
conditions
provide
greater predictive accuracy than environmental cues, ge-
netic
polymorphism
can
be
favoured,
along
with
genes
that
are
selected
to
modify
phenotypic
development
appropri-
ately for each genetic morph [7] (such ‘specific’ modifiers
are known;
e.g.,
from
studies
of
sex
determination
[16]).
Thus by taking such an explicitly informational approach
Opinion
0169-5347/
2015Elsevier Ltd. All rights reserved. http://dx.doi.org/10.1016/j.tree.2015.04.002
Corresponding author: Dall, S.R.X. ([email protected]).
Keywords: development; information; genetic cues; epigenetic effects; environmental
cues.
TREE-1935; No. of Pages 7
Trends in Ecology & Evolution xx (2015) 1–7 1
8/9/2019 Trends Ecol Evol (Amst) 2015 Dall SR
http://slidepdf.com/reader/full/trends-ecol-evol-amst-2015-dall-sr 2/7
we
can
predict
epistatic
effects
among
genes
determining
the cue
integration
(developmental)
system
and
other
genes
that
provide
cues.
This informational perspective offers a powerful way to
understand
how
genetic
and
epigenetic
influences
are
integrated
during
development.
Since
this
perspective
was introduced [6,7,10] it is increasingly being used to
interpret
a
wide
variety
of
biological
phenomena
[3,5,17–21]. Here we promote the scientific value of this approach
by
outlining
the
underlying
logic
and
detailing
how
it
can
elucidate
taxonomically
widespread
phenomena.
We
show
how rigorously applying Darwinian logic at an organismal
level
(i.e.,
assuming
selection
favours
developing
pheno-
types that process information to maximise their fit to their
local
environment)
can
help
to
explain
genetic
influences
on phenotypic
variation
in
novel
and
counterintuitive
ways.
Being alive can be informative
Central to the idea that genes can be used as developmen-
tal
cues
of
the
forthcoming
environment
is
the
existence
of
persistent genetic variation with alleles differing in fre-quency
in
different
environments
[7,22].
If
the
ability
to
cope with local environments is (to some degree) controlled
genetically
and
conditions
remain
stable
enough
across
generations
(e.g.,
individuals
are
likely
to
inherit
parental
environments and do not disperse too far away to repro-
duce),
the
fact
that
an
individual
exists
suggests
that
it
is
likely
to
be
in an
environment
to
which
it
is
well
adapted.
This is because most of the individuals of its genotype are
likely
to
be
born
into
such
‘good’
habitats
precisely
because
genotype
fitness
(the
rate
at
which
it
is
copied)
is
max-
imised where it is best matched to environmental condi-
tions.
Thus,
over
generations,
genotype
members
will
accumulate
disproportionately
in
environments
to
whichthey
are
well
suited
[10,21]. We
call
this
demographic
accumulation the ‘Multiplier Effect’ (ME) and have dem-
onstrated
how
it
can
explain
the
evolution
and
mainte-
nance of
ostensibly
paradoxical
unconditional
strategies
such as natal philopatry (attempting to breed in natal
habitats)
[10]. We
briefly
illustrate
the
main
insights
(modelling
details
can
be
found
in
[10]).
Case
study:
natal
philopatry
Consider an organism with discrete, non-overlapping gen-
erations with a 1-year generation time. The environment
contains many breeding sites, some of which are good (it is
well
suited
to),
others
poor.
Sites
change
quality
over
time
but
site
quality
(good
or
poor)
is
positively
correlated
between years. During development individuals receive
environmental
cues
of
current
site
quality.
Individuals
can either
attempt
to
breed
on
their
birth
site
or
choose
another breeding site at random. After breeding the indi-
vidual
dies
and
its
offspring
face
the
same
decision.
Consider
first
a
genotype
that
ignores
environmental
cues and always attempts to breed at its birth site (i.e., is
natally
philopatric).
Since
good
sites
produce
more
surviv-
ing offspring
than
poor
sites,
by being
natally
philopatric
individuals
of
the
genotype
increase
their
chances
of
breed-
ing on a good site. Over generations this effect amplifies
(the
ME
[10]). This
results
in
a
higher
proportion
of
individuals
breeding
on
good
sites
at
demographic
equilib-
rium
than
would
be
expected
by
chance
given
the
frequency
of
good
sites
in the
environment.
Therefore,
breeding
on
birth sites is the best thing for individuals to do unless
environmental
cues
provide
very
strong
evidence
that
sites
are
poor.
In
other
words,
natal
philopatry
maximises
fitness unless environmental cues are highly accurate
(Figure 1). In
informational
(Bayesian)
terms
[23,24],the probability that an offspring came from a good site
acts
as
the
Bayesian
prior
and
the
posterior
probability
is
the
probability
of a
good
site
given
this
prior
and
the
cue.
Since an individual that does not attempt to breed at its
natal
site
chooses
a
site
at
random,
natal
philopatry
is
optimal provided the posterior probability exceeds the
proportion
of
good
sites
in
the
environment.
As
Figure
1
shows,
the
likelihood
that
natally
philopa-
tric individuals came from good sites (the Bayesian prior)
depends
strongly
on
the
ratio
of
surviving
offspring
on
the
two
site
types.
This
ratio
might
depend
on
other
aspects
of
the genome. If variation in these other aspects were main-
tained,
it
would
be
adaptive
to
have
a
cue
integration
(e.g.,
developmental) system that based its ‘decision’ on whetherto disperse
on
both
the
cue
value
and
cues
provided
by
these other genetic elements. In other words, one might
expect
epistasis
between
the
genes
controlling
the
cue
integration
system
and
those
affecting
the
ratio
of
surviv-
ing offspring produced on different patches.
There
has
been
a
recent
effort
to
link
ideas
about
the
ME
[10]
to
a
branch
of
population
genetics
theory
that
has
its roots in Fisher’s thinking about mutation–selection
balance
[21]. According
to
the
Reduction
Principle
(RP),
0
0.2
0.4
0.6
0.8
1 1.5 2 2.5 3 3.5 4
P r o b a b i l i t y
p a t c h
i s g o o d
Gain rao (good/poor)
e = 0.2
e = 0.025
e = 0.05
e = 0.1
TRENDS in Ecology & Evolution
Figure 1. Effect of the ratio of the numbers of surviving offspring on good sites to
numbers on poor sites on natal philopatry and the ‘Multiplier Effect’. The broken
line shows the probability that a randomly chosen site is good. The curves show
the posterior probability that the natal site is good given that the developmental
cue indicates a bad site (i.e., is 0; see below). It is optimal to ignore this cue if the
posterior probability exceeds the probability that a randomly chosen site is good.
Good sites remaingoodfor 10 yearson averagebeforeturning poor and poor sites
persist for 40 years before becoming good; the proportion of good sites in the
environment is 0.2. During development each population member receives a cue
thatis either0 or1. Ifthe siteis poor, the cue is0 withprobability1 – e and is1 with
probability e (where 0 < e < 0.5). If the site is good, the cue value is 0 with
probability e and is 1 with probability 1 – e . If e is greater than thecriticalcue error,
probability fitness is maximised by ignoring cues and being natally philopatric.
Individuals that attempt natalphilopatryfail to do sowith probability0.04. Thereis
no density dependence acting, althoughMcNamara andDall [10] showthat similar
results can be obtained if it is included. Adapted from [10].
Opinion Trends in Ecology & Evolution xxx
xxxx,
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populations
near
an
equilibrium
between
selection
and
any
‘transformation
processes’
(e.g.,
mutation,
dispersal,
re-
combination)
will
evolve
less
transformation
because
at
such an equilibrium any change in phenotypic state (e.g.,
where
individuals
are,
what
alleles
they
express)
is
likely
to
be
a
change
away
from
matching
the
selective
environ-
ment (i.e., maladaptive) as most individuals will already be
in
conditions
to
which
they
are
suited
[21]. It
can
be
shownthat the conditions under which the ME operates are
equivalent
to
those
specified
by
the
RP
[21]; therefore,
the genetic
cue
approach
is
also
likely
to
provide
insight
into the evolution of a wide range of population genetic
phenomena
including
modifier
loci,
linkage
disequilibri-
um, recombination, evolvability, and dispersal or migra-
tion
(reviewed
in
[21]). Thus,
we
might
expect
lower
mutation
or
recombination
rates
to
evolve
when
fitness
landscapes are rugged and do not vary much between
generations
as
this
makes
it
likely
that
any
phenotypic
change
would
be
maladaptive
[10,21].
Applying the ‘genetic cue’ perspective
Phenomena involving cue integration are taxonomically widespread.
To
further
illustrate
the
value
of
the
genetic
cue perspective, we discuss two examples where predation
or
herbivory
intensity
varies
and
individuals
can
invest
in
costly
defences
based
on
information
from
various
sources.
For instance, defences in both crustaceans and plants can
be
induced
by
individual
experience
and
maternal
cues.
Here
we
show
that
genetic
cues
are
also
likely
to
play
a
role.
Many
species of Daphnia
develop distinct
defensive
morphologies
against predators,
usually in response
to
waterborne chemical cues of predator presence (e.g.,
predatory
phantom
midge larvae kairomones). For Daph-
nia pulex these
defences include
dorsal
‘neck
teeth’ andtheir induction has been
studied in considerable detail
[25–30]. Phantom midge larvae are gape-limited preda-
tors and it is mainly juvenile daphnids
(up
to
the
fourth
instar)
that are vulnerable
to
them.Correspondingly, the
neck teeth arepresent during instars one to four and tend
to
bemost
strongly
expressed
in the third instar
[27].
The
development
of
neck teeth
in response
to
kairomones
can
be viewed as cue integration. If mothers experience kair-
omones,
but not their offspring, offspring
express neck
teeth mainly in the second instar [27]. Furthermore,
offspring have a developmental window for induction of
neck teeth, during the late embryonic stage [29] while in
maternal brood
chambers. Without
exposure to
kairo-
mones
then,
neck teeth
are not expressed.
If
offspring
experience kairomones in time, the degree of neck tooth
expression
depends
on
the strength
and
duration
of
kai-
romone
exposure [27,29]. Thus,
from
a
developmental cue
integration perspective, there should be an early indica-
tion
that defence
is needed,
through maternal or
embry-
onic experience,
and,
given
this, the strength
of
defence
investment depends on continued evidence that it is
needed. We
can extend
this to
include
genetic cues
as
follows.
There
is
substantial
variation
in
how
readily
individua-
ls induce defences, even among clones collected from the
same
ponds
[26,28]. Given
that
daphnids
go
through
bouts
of asexual reproduction
interspersed
with
episodes
of
sex,
there is ample opportunity
for
locally adapted
ge-
netic variation
to
accumulate
at different times
and in
different microhabitats. Thus, prevailing genotypes are
likely to
cue (correlate with) local conditions (e.g., local
abundance of
predators)
in a
similar way as
maternal
cues [5]. For instance, D. pulex clones taken when phan-
tom midge larval densities were at their highest fre-quently induced defensive morphologies at very low
kairomone concentrations,
while clones
taken when
phantom
midge
larvae
were
rare and fish predators
predominated showed weaker responses (few individuals
induced
defences, and only at higher
kairomone concen-
trations) [26]. The informational interpretation is that
the former clones
had high
inherited (genetic)
expecta-
tions of
predation
risk
by
phantom midge
larvae
and
therefore did not need much corroboration from environ-
mental cues to
develop
defences,
while the latter clones
had very
low
phantom midge predation risk
expectations
and therefore required stronger environmental evidence
to
induce defences. To date there have been
no empirical
tests of this explanation for variation in the inducibility of defences
in
daphnids.
In
the field,
clones
could be
sampled across their spatiotemporal niches (different
places
and different
seasons)
to
ascertain whether they
show
reaction norms that
on
average are
favourable
for
the conditions encountered. Laboratory manipulations of
the requisite spatial
and temporal variation in predation
risk would also
be
feasible.
Plants often induce biochemical defences in response to
insect
herbivory
[31]. In
addition,
it
has
been
suggested
that
antiherbivore
defences
might
commonly
be
induced
transgenerationally [32,33]. One reason to expect adaptive
maternal
effects
to
evolve
in
plants
is
that
pollen
dispersal
often
occurs
over
much
greater
distances
than
seed
dis-persal,
possibly
inhibiting
local
genetic
adaptation
and
favouring epigenetic signalling from mother plants to
seeds
[9,34,35].
There
are
numerous
molecular
mecha-
nisms
of
the
induction
of
plant
defences
involving
the
jasmonate signalling pathway that are being actively ex-
plored.
These
include
direct
responses
to
plant
tissue
wounding
[31]
and
transgenerational
induction
involving
small-RNA signalling from mother plant to seeds [32,33] as
well
as
genetic
(ecotypic)
variation
in
defence
[36]. Box
1
illustrates how integration of these different effects can
evolve, if they are explicitly regarded as potentially infor-
mative cues during development. See [5,9] for other exam-
ples
of
similar
evolutionary
models.
The novel
interpretation
we
argue
for
in
both
cases
above – that an individual’s genotype can serve as a cue
of
the
risk
of
predation
or
herbivory
in
the
near
future
–
has
so
far
not
been
tested
empirically.
Such
tests
would
be
important, because they can increase our understanding of
the
circumstances
that
favour
genetic
versus
environmen-
tal
determination
of
phenotypes
and,
more
generally,
the
integration of information during development. In contrast
to
traditional
approaches
to
the
study
of
phenotypic
plas-
ticity
and
genetic
polymorphism,
our
approach
allows
these
phenomena
to
be
conceptualised
within
a
common
framework, thereby facilitating predictions of the use and
integration
of
cues.
Opinion Trends in Ecology & Evolution xxx
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Box 1. Plant defence induction against herbivory
Figure I i llustrates a simulation model of the induction of plant
resistance against herbivory as motivated in the main text, which
follows the general scheme outlined by Holeski et al. [33]. Local
patches vary spatially and temporally in the expected intensity of
herbivore attack, which can be either low or high. The defence
phenotype expressed in the mature plant u protects the plant by
changing herbivore consumption by a factor 1 – u but has the cost of
changing the
reproductive output of the unconsumed parts of theplant by 1 – u /2. In the model, herbivore attack acts both as an
environmental cue that induces defence and as a selective factor
(Figure IA). A maternal cue can also beproducedby the plant, priming
the seeds for defence induction, and it is possible for herbivory
intensity-correlated genetic variation in u (‘genetic cues’) to accumu-
late under certain conditions (see below). Performing evolutionary
simulations under various conditions, we explore the
extent to
which u is influenced by genetic, maternal, and direct environmental
cues (see the supplementary material online for modelling details).
We show that defences can be induced as a response to a
combination of maternal and environmental cues (Figure IB), a
combination of genetic and environmental cues (Figure IC), or just
environmental cues (Figure ID). These outcomes depend on which
influences can convey information about the likely herbivory
intensity, given temporal and spatial variation in conditions andgeneflow, and on the availability of mechanisms of cue transmission.
‘Genetic cue use’ (genetically polymorphic antiherbivore defences) is
predicted when there is substantial genetic variation among patches
at evolutionary equilibrium (e.g., Figure IC: very high patch temporal
stability and very limited seed andpollendispersal) and therefore cue
locus allele frequencies better predict the risk of herbivory than noisy
maternal cues.
Pollen Ovule
Maternal cueSeed
Seed dispersal
Growing plant Herbivory
Jasmonate signalling
Mature plant Herbivory
(A)
–1.0
0.0
1.0
0.0
0.2
0.4
0.6
0.8
1.0
Maternal cue
D e f e n s e
p h e n o t y
p e
(B)
–1.0
0.0
1.0
0.0
0.2
0.4
0.6
0.8
1.0
Genec cue
D e f e n s e
p h e n o t y p e
(C)
0.0 1.0
0.0
0.2
0.4
0.6
0.8
1.0
Herbivory cue
D e f e n s e
p h e n o t y p e
(D)
TRENDS in Ecology & Evolution
Figure I. Evolution of inducible defences against herbivory in diploid hermaphroditic plants. See the supplementary material online for further details. (A)
Sketchof the
life history and information flow to themature plant.Ovules arefertilisedby dispersingpollen and seeds receive genetic cues (alleles at a cuelocus) from each parentas
well as small RNA-mediated epigenetic cues from themother plant. After seed dispersal the growing plant might be fedupon,which influences the level of jasmonate
signalling and is a cue of the risk of herbivory for the mature plant. (B–D) Evolutionaryequilibria in defence levels. (B) High temporal stability of herbivory, very limited
seeddispersal, and freeamong-patchpollendispersal. Thegreycurve shows the average induceddefenceas a functionof thematernalepigenetic cue.The points show
induceddefencesof individual plants in low (blue) andhigh(red) expectedherbivory patches. Thedeviationof thepoints from thegreylineis a responseto theintensity
of herbivory on thegrowing plant. There is little genetic variation in defence. (C) Very high temporal stability and very limited seed and pollen dispersal, together with
very noisy transmission of thematernal cue, results in an equilibrium with substantial genetic variationat thecue locus,whichapproximately correspondsto the three
genotypes of an additive two-allele locus. Deviations from the grey line are responses to the intensity of herbivory on the growing plant. There is little maternal
influence on thelevel of defence.(D) High temporal instabilitywith lowand high herbivory intensity varying randomlyacross generations,in which case only thedirect
environmental cue (herbivory on the growing plant) influences induced defences.
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New perspectives on dominance, epistasis, and genetic
conflict
For genes
that encode developmental systems,
the geno-
type at a genetic cue locus can play a similar role as
environmental cues, in thesense
of providing
information
to
the organismabout selectively relevant circumstances.
Based on this view of genes as cues of the selective
environment,
we should expect systems that fine-tunedevelopment to genetic variation to evolve [7,22]. This
can occur
via selection
for
genetic modifiers that adjust
developmental
trajectories
[12,15]. For
instance, if the
different homozygotes at a two-allele locus are adapted to
markedly different
environmental conditions and
there is
substantial gene flow in the population, the phenotype of
the heterozygote
is likely to
evolve
to
match one of
the
homozygotes (e.g.,
the most commonly
adaptive one).
This will occur through the invasion of modifier loci that
change
the phenotype of
the heterozygote
[37].
Thus
dominance
can be viewed
as evolving via the fine-tuning
of the developmental influence of genetic cues of the
selective environment [22].
Another consequence of viewing developmental sys-tems as potentially
using genetic cues
is that genetic
conflict [38] is likely to play a significant role in the
evolution of
these
systems
[7].
To see why this is so,
consider
two
habitats
with
different phenotypes
being
optimal in each habitat and, for simplicity, haploid indi-
viduals that reproduce sexually. If
there is a
two-allele
locus with
alleles
producing
phenotypes that are suitable
for each habitat, depending on the intensities of selection
and gene flow allele frequencies
will differ
between habi-
tats.
Potential modifiers that
are fully linked
to
an allele
that is common in one habitat and rare in the other will
mainly experience
one of
the habitats, so
their evolution-
ary ‘interest’
will be to
produce
a
phenotype
that is
suc-cessful in that habitat.
For
unlinked
modifiers, however,
thesituation canbe radically different. Amodifier allele at
an unlinked
locusmight be present
at similar frequencies
in both
habitats
and its
evolutionary interest will be to
produce phenotypes that do well overall. Therefore, un-
linked
modifiers
that produce
less extreme
phenotypes
will be favoured.
It
is even
possible that
unlinked
modi-
fiers favour genetically monomorphic generalist pheno-
types whereas fully linked
modifiers favour genetic
polymorphisms. Such differences in the evolutionary
interests of modifier genes with contrasting linkage to a
genetic cue locus represent genetic conflict [38]; evolution-
ary change
favoured
by linked
modifiers (increased
phe-
notypic divergence
between morphs) selects
for unlinked
modifiers to reverse this change.Aswell asless phenotypic
differentiation, unlinked modifiers can
favour
develop-
ment that
is sensitive
to
environmental cues [7],
in effect
favouring phenotypic plasticity over genetic polymor-
phism. The evolutionary outcomes
of
such ecologically
driven
genetic conflicts will depend
on
the mechanisms
of regulation of development and gene expression. In
general,
the genetic cue
approach highlights the need
for
further work on
ecologically driven
genetic conflicts,
having the potential
to
predict
patterns
of
linkage
and
epistasis in phenotype determination from Darwinian
first principles.
A Darwinian framework for development:
ecoevolutionary
feedback
is
key
Since
the
informational
interpretation
of
genotypes
was
introduced in the literature [6,7], it has attracted the
interest
of
researchers
exploring
a
range
of phenomena,
including
phenotypic
polymorphisms
(polyphenisms
[39]),
transgenerational epigenetic influences on development
[9,40],
mechanisms
of
ageing
[17], sex-determination
sys-tems [20,41], early-life influences on health and disease
[18], genetic
variation
in
stress
sensitivity
[19], and
eco-
logical
responses
to
anthropogenic
environmental
change
[42]. To encourage wider application, we encapsulate its
basic
logic
in
a general
informational
(Bayesian)
frame-
work [23] for development in Figure 2. Such approaches
embody
fundamental
Darwinian
logic
since
fitness
is
max-
imised
by
phenotypes
that
maximise
their
fit
to
current
conditions by utilising any sources of information available
when
it
is
cost-effective
to
do
so
[43].
A
crucial
feature
of
an
ecologically
consistent
[44,45]
informational framework for development is that it must
incorporate
various
ecoevolutionary
feedbacks.
Two
are
illustrated in Figure 2. If
an
environmentvaries
spatially,
thedistribution
across
habitats of individuals can be regarded as a Bayesian
prior distribution
for
the developmental
system they
possess. Local cues
during
development
provide further
information on local conditions. However, the manner
in
which
such
cues
modify
development
affects
how the
survival
and
reproduction
of
individuals
depend
on
local conditions, determining the spatial distribution of
individuals and hence the prior
distribution
itself.
Developmental
system Phenotype
Distribuon of
individuals acrosslocal habitats
Correlaon between
cue genes and
environment
Local
habitat
Cue genes
Parental
states
TRENDS in Ecology & Evolution
Figure 2.
A Darwinian framework for integrating genetic and epigenetic
information during development. We envisage environments comprising local
habitats linked by dispersal. Conditions can vary among habitats and over time.
Thelocal habitat, parental states, and genes allprovide cues that areintegrated by
the developmental system to determine the mature phenotype. The
developmental system is under selection to match phenotypes to environments.
The distribution of individuals across habitat types is determined by the
demographic processes of survival, reproduction, and dispersal. It is thus
influenced by the developmental system itself, through the phenotypes that
develop in different conditions. At phenotypic determination (during
development), this distribution acts as a Bayesian prior distribution on habitat
type. Given a cueof local conditions during development, the posterior probability
that the local habitat is of a given type depends on the developmental system.
Thus, selection on the developmental system to change its responses to
environmental cues depends on its existing configuration.
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At evolutionary stability the developmental system will
integrate
prior
information
anddevelopmental
cues
in
an
optimal
way
given
the prior
distribution resulting from
its particular mechanism for phenotype determination.
The
correlation
between
cue
genes
and
the
local
selective environment imposes selection on the cue
genes
themselves
and
how
they
are
integrated
by
the
developmental
system.
The
correlation
depends
on
the
developmental process itself; it will typically be low
when developmental systems ignore genetic cues, sincecue
genes
are
then
under
weak
selection,
and
higher
when phenotypes
depend
more
on
such
cues.
Thus
the
information
content
of
genetic
cues,
and
hence
the
selection pressure on developmental systems to inte-
grate
these
cues,
depends
on
the
developmental
system
itself. Again, at evolutionary stability the developmen-
tal system should be optimal given the selection
pressures
it
generates.
Such
feedback
raises
the
possibility
that
there
might
be
more
than
one
evolutionarily
stable
developmental
system
in any given environment.
Concluding
remarks:
empirical
and
philosophical
prospects
Substantial empirical effort remains to fully understand
any developmental
process
underpinning
phenotypic
vari-
ation
from
an
adaptive
perspective.
Our
framework
(Figure 2) lends itself naturally to generating hypotheses
that
are
testable
using
the
‘modern
toolkit’
of
approaches
for
studying
adaptation
in
evolutionary
biology.
To
illus-
trate
how
it
could
be
applied
we
give
a
few
examples
of
promising areas of inquiry in Box 2.
A major
challenge
in
modern
biology
remains
to
fully
understand
how
genetic
variation
maps
to
phenotypic
variation. We offer our developmental cue integration
framework
(Figure 2) as
a
powerful
basis
for
theorising
about
the
links
between
genotype
and
phenotype
in
Dar-
winian systems. There are important philosophical impli-
cations
of
this
perspective
[8,46,47].
The
idea
that
both
genetic and environmental cues are ‘read’ by the mecha-
nisms
of
development
to
maximise
phenotypic
‘fit’
to
the
environment demonstrates that thinking of inheritance
systems such as the genome as representing (biased sub-
sets of) environments has considerable explanatory utility in biology [47]. We are confident that explicitly informa-
tional
approaches
to
understanding
biological
systems,
centred
on
phenotypes
as
evolved
information-processing
systems, can offer profound new insights.
Acknowledgements
The authors thank Angus Buckling, Brian Charlesworth, Tim Coulson,
Peter Hammerstein, Andrew Higginson, Dave Hosken, Dustin Ruben-
stein, Judy Stamps, Tom Tregenza, Tobias Uller, and Nina Wedell for
helpful feedback. This work was supported by a Leverhulme Trust
International Network Grant to S.R.X.D., Peter Hammerstein, O.L., and
J.M.M., as well as grants from the Swedish Research Council (621-2010-
5437)
and the Strategic Research Program
Ekoklim at Stockholm
University to O.L.
Appendix A. Supplementary dataSupplementary data associatedwith thisarticle canbe found,in theonline
version, at http://dx.doi.org/10.1016/j.tree.2015.04.002.
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