Tracing the trajectory of behavioral impairments and oxidative stress in an animal model of neonatal...
Transcript of Tracing the trajectory of behavioral impairments and oxidative stress in an animal model of neonatal...
Neuroscience 298 (2015) 455–466
TRACING THE TRAJECTORY OF BEHAVIORAL IMPAIRMENTSAND OXIDATIVE STRESS IN AN ANIMAL MODEL OF NEONATALINFLAMMATION
M. MACRAE, a T. MACRINA, a A. KHOURY, b
M. M. MIGLIORE b AND A. C. KENTNER a*
aSchool of Arts & Sciences, Health Psychology Program,
MCPHS University (formerly Massachusetts College of Pharmacy
& Health Sciences), Boston, MA 02115, United States
bSchool of Pharmacy, MCPHS University, Boston, MA 02115, United
States
Abstract—Exposure to early-life inflammation results in
time-of-challenge-dependent changes in both brain and
behavior. The consequences of this neural and behavioral
reprogramming are most often reported in adulthood.
However, the trajectory for the expression of these various
changes is not well delineated, particularly between the
juvenile and adult phases of development. Moreover, inter-
ventions to protect against these neurodevelopmental dis-
ruptions are rarely evaluated. Here, female Sprague–
Dawley rats were housed in either environmental enrich-
ment (EE) or standard care (SC) and their male and female
offspring were administered 50 lg/kg i.p. of lipopolysaccha-
ride (LPS) or pyrogen-free saline in a dual-administration
neonatal protocol. All animals maintained their respective
housing assignments from breeding until the end of the
study. LPS exposure on postnatal days (P) 3 and 5 of life
resulted in differential expression of emotional and cogni-
tive disruptions and evidence of oxidative stress across
development. Specifically, social behavior was reduced in
neonatal-treated (n)LPS animals at adolescence (P40), but
not adulthood (P70). In contrast, male nLPS rats exhibited
intact spatial memory as adolescents which was impaired
in later life. Moreover, these males had decreased prefrontal
cortex levels of glutathione at P40, which was normalized in
adult animals. Notably, EE appeared to offer some protec-
tion against the consequences of inflammation on juvenile
social behavior and fully prevented reduced glutathione
levels in the juvenile prefrontal cortex. Combined, these
time-dependent effects provide evidence that early-life
inflammation interacts with other developmental variables,
specifically puberty and EE, in the expression (and preven-
tion) of select behavioral and molecular programs.
� 2015 IBRO. Published by Elsevier Ltd. All rights reserved.
http://dx.doi.org/10.1016/j.neuroscience.2015.04.0480306-4522/� 2015 IBRO. Published by Elsevier Ltd. All rights reserved.
*Corresponding author. Tel: +1-617-274-3360 (O); fax: +1-617-732-2959.
E-mail address: [email protected] (A. C. Kentner).Abbreviations: ANOVA, analysis of variance; EDTA,ethylenediaminetetraacetic acid; EE, environmental enrichment; LPS,lipopolysaccharide; MIA, maternal immune activation; P, postnatal day;SC, standard care.
455
Key words: inflammation, maternal care, enrichment, devel-
opment, oxidative stress, corticosterone.
INTRODUCTION
Exposure to inflammatory mediators at distinct critical time
periods (i.e., fetal or neonatal development) results in long-
term brain changes and corresponding behavioral
disruptions in rats and mice. The occurrence of such
disruptions is dependent on the timing of early-life
challenge and has been reported most often in mature
animals (Meyer et al., 2006a, 2008b).Moreover, the conse-
quences of reprogramming the brain following exposure to
inflammatory mediators such as lipopolysaccharide (LPS)
and polyriboinosinic–polyribocytidilic acid (Poly:IC) appear
to have a regulated time course (Harre et al., 2008; Forrest
et al., 2012; Garay et al., 2013; Khalil et al., 2013; Liu et al.,
2013). For example, neonatal (n)LPS led to hippocampal
NMDA receptor subtype expression that was juxtaposed
between acute (i.e., increased expression) and chronic
(i.e., decreased expression) time points (Harre et al.,
2008). Time-dependent emergence of behavioral impair-
ments is also apparent between adolescence and adult-
hood (Fan et al., 2011; Stolp et al., 2011; Dinel et al.,
2014). Mice challenged with nLPS had increased anxiety-
like behavior at postnatal day (P)30 that was resolved by
P90. The opposite expression pattern was observed with
respect to depressive-like behavior in the forced swim test
(Dinel et al., 2014) while repeated nLPS i.p. injections in
rats were associated with increased duration and number
of entries into the light chamber of the light/dark test in
adulthood, but not at P21. The reverse was seen with
respect to disrupted prepulse inhibition response at P20,
which was not sustained following maturity (Stolp et al.,
2011). In general, the time course of behavioral and neural
manifestations following early inflammatory stressors is
not well understood. Therefore, in the present paper, we
incorporate both juvenile and adult developmental time
points into the evaluation of reprogramming following
nLPS.
The developmental disruptions that follow some
inflammatory challenges are interesting given their
similarities to the timing and phenotypical expression of
autism and schizophrenia, particularly with respect to
cognitive functioning (Zuckerman et al., 2003; Meyer
et al., 2006b; Boksa, 2010). The parallels in the
456 M. MacRae et al. / Neuroscience 298 (2015) 455–466
pathogenesis between these neurodevelopmental disor-
ders and early-life inflammation also extend to social
impairments, imbalances in dopamine, reductions in
reelin and NMDA receptor expression, in addition to dys-
regulation in immune system mediators such as cytoki-
nes, chemokines and other chronic modifications
precipitated by immune activation (Coyle et al., 2003;
Meyer et al., 2008a; see Shi et al., 2003; Patterson,
2009). Notably, oxidative stress has been proposed as a
mechanism underlying disruptions in animal models of
immune activation, as well as schizophrenia and autism
(Do et al., 2000; Boksa, 2010; Gu et al., 2015).
Maternal immune activation (MIA) induces oxidative
stress in fetal brain and the depletion of glutathione, which
protects cells from oxygen-free radicals. Pretreatment
with the antioxidant N-acetylcysteine increases
L-cysteine levels, prevents LPS-induced decreases in
fetal glutathione (Lante et al., 2007; Paintlia et al.,
2008), and protects against associated deficits in juvenile
spatial memory (Lante et al., 2007).
Environmental enrichment (EE) protocols have
demonstrated success as an intervention for autism and
schizotypal personality in human rehabilitation settings
(Raine et al., 2003; Woo and Leon, 2013), and a clinical
trial is currently in progress evaluating EE for infants at
risk for cerebral palsy (Morgan et al., 2014). Recently,
EE prevented social interaction impairments and hypotha
lamic–pituitary–adrenal activation following MIA (Connors
et al., 2014). Moreover, there is evidence for enriched
environments preventing/reducing oxidative stress in ani-
mal models of cerebral hypoperfusion (Cechetti et al.,
2012), Alzheimer’s disease (Herring et al., 2011), and
aging (Kempermann et al., 2002), each of which are asso-
ciated with inflammatory activation. Therefore, we
employed EE in order to evaluate its ability to counteract
oxidative stress and behavioral disruptions in a dual-
administration nLPS model. Overall the purpose of this
paper was to (1) map out the developmental timing of
the emerging brain and behavioral impairments following
neonatal inflammation, and (2) evaluate the protective
effect of the environment against these behavioral disrup-
tions and reductions in glutathione, an indicator of oxida-
tive stress.
EXPERIMENTAL PROCEDURES
Animals and housing
Virgin female and male Sprague–Dawley rats were
obtained from Charles River (Wilmington, MA, USA) and
housed at 20 �C on a 12-h light/dark cycle (0700–1900
light) with free access to food and water. Female rats
were pair-housed in one of two conditions: EE (large
multi-level cage with toys, tubes, chew bone, Nestlets�and ramps; Critter Nation, Muncie IN, USA), or
Standard Care (SC; standard cage with tube, chew
bone, and Nestlets�). Toys and tubes were changed
twice weekly in the EE group to ensure novelty of the
condition. Male rats were maintained in standard
housing. Experimental procedures were approved by
the MCPHS University Institutional Animal Care and
Use Committee and were carried out in compliance with
the Association for Assessment and Accreditation of
Laboratory Animal Care (AAALAC). A flowchart of the
study procedures is located in Fig. 1.
Breeding, parturition and litter phenotype
Following acclimatization to laboratory conditions female
rats were bred and pregnancy was confirmed by
continued weight gain and visible teats during the later
phase of gestation. Approximately two days prior to
parturition, SC dams (n= 12) were placed into
individual cages and EE females (n= 8; one female
was not pregnant for a final n= 7) were separated from
their partner, in a cleaned cage, by a physical divider
that allowed for olfactory, auditory, and some tactile and
visual contact. This separation allowed for the correct
identification of dams and their litters after birth
[postnatal day (P)1] and was maintained until weaning
(P22).
On P3 all litters were adjusted to 12 pups, creating an
equal distribution of males and females wherever
possible. A dual lipopolysaccharide (LPS; Escherichiacoli, serotype 026:B6; L-3755, Sigma, St. Louis, MO,
USA) administration protocol was used on P3 and P5.
Pups were injected i.p. with 50 lg/kg of LPS or an
equivolume of pyrogen-free saline, in a balanced
manner within litters. Their skin was then colored with
non-scented non-toxic markers in order to identify the
neonatal drug treatment received (described previously
Connors et al., 2014). Weaning involved the removal of
each dam and placing her offspring into a clean cage,
maintaining their respective neonatal housing conditions.
EE offspring were housed in same-sex groups of four–six
while SC animals were housed in pairs; all animals were
weighed once per week following weaning.
Maternal behavior
In order to ensure that the nLPS protocol did not influence
maternal behavior we monitored passive maternal care
between P3 and P6, three times daily (7:30, 12:30,
17:30 h); each session consisted of ten observations and
a total composite score was calculated for each postnatal
day. Dams (n= 12 SC; 7 EE) were evaluated for 1-min
intervals per observation (with at least 5 min between
each interval). Behaviors scored included the frequency
of licking/grooming, pup retrieval, and nest building
(digging, retrieving Nestlets� to the nest), in addition to
high arched-back, low arched-back (blanket) and passive
nursing (dam lying on either her back or side). Finally, the
total duration of time on the nest was recorded.
On P7 we employed a maternal preference test. Four
rat pups from each neonatal treatment/sex were grouped
together in different areas of a large arena (72 cm �72 cm � 36 cm). Large amounts of home cage nesting
material were placed in one section of the arena, equal
distance from the location of each pup group. Dams were
then placed into this arena and latency to retrieve
(seconds) was recorded. Surprisingly, few dams from
either housing condition demonstrated retrieval behaviors
so we only evaluated a subset of the original set of dams
(n= 6 SC; 7 EE). Post hoc, we simply measured the
Fig. 1. Flow chart of study procedures.
M. MacRae et al. / Neuroscience 298 (2015) 455–466 457
percentage of time dams spent in direct contact (sniffing,
standing over, nursing, licking) with each neonatal
treatment group/sex (total seconds spent with group/600
second test) * 100. Given the failure of dams to retrieve in
the maternal preference test, we evaluated maternal
retrieval times in the home cage (n= 12 SC; 7 EE).
From each litter, two pups from every neonatal
treatment/sex were scattered across the home cage
floor. Latency to begin retrieval and total time to collect all
pups from the litter (and each group) back to the nest
were logged. Maternal anxiety level was also evaluated in
an open field test for 10 min (n= 12 SC; 6 EE). One EE
rat was not tested in the maternal anxiety test due to
experimental error. The black plexiglas open field arena
(40 cm � 40 cm � 28 cm) was divided into a 25-square
grid. The percentage of entries into the center of the open
field [(central entries/total entries) � 100] was calculated
as an index of anxiety level (Paris et al., 2011). For the
remainder of the study, only one pup per sex and neonatal
treatment groupwas used per litter for each behavioral and
molecular time point described below.
Offspring behavior
Social behavior and spatial memory were evaluated in
male and female offspring, in a counter-balanced
manner on P40 (n= 7–10) and P70 (a separate group
of rats; n= 6–10). Beforehand, rats were habituated to
a black test arena (40 cm � 40 cm � 28 cm), over three
separate days, for 10 min daily. The discrepancy
between the total number of litters and offspring
evaluated in the behavioral tests is due to a file transfer
failure between the video camera and computer, which
resulted in data loss.
Social interaction: To evaluate social behavior, rats
were introduced to a novel SC-housed conspecific
(n= 8) of the same sex and age, for 10 min in an
identical manner as used previously by this laboratory
(Connors et al., 2014). In brief, we evaluated animals on
the frequency and duration of each of the following behav-
iors: allogrooming, mounting/crawling, approaching/fol-
lowing. We categorized these observations into
composite scores to detail the total duration of time spent
initiating vs. receiving social contact.
Object-in-place: A novel object was positioned in each
corner of the arena and rats were given 5 min to explore.
After a 1-h delay objects were replaced with identical
copies of the four items, except that the placement of
two of the objects switched location. Animals were
returned to the arena for an additional 5 min of
exploration (as described in Connors et al., 2014). A dis-
crimination ratio was calculated [(total time exploring
moved objects � total time exploring permanent
objects)/(total time exploring both objects)].
Blood sampling and plasma corticosterone
One week following the P70 behavioral tests, a random
sample of adult rats (n= 5–6) were restrained in a
plastic cone for 10 min, following a baseline tail blood
collection. At baseline, the rat’s tail was lanced close to
the tip and a microvette (CB 300 K2E; Sarstedt,
Germany) was used to collect tail blood. The microvette
was coated with EDTA to prevent coagulation of blood.
Tail blood samples were collected at 15, 30, 60, and
120 min following restraint. Samples were kept on ice,
centrifuged and plasma aliquots were stored at �75 �Cuntil processing. Blood sampling took place between
10:00 and 1:00 pm to limit potential circadian rhythm
effects. Plasma corticosterone levels were measured in
duplicate by ELISA according to the small sample assay
protocol of the standard testing kit (ADI-900-097, Enzo
Life Sciences, Farmingdale, NY, USA). The minimum
detectable concentration was 26.99 pg/ml, and the intra-
and inter-assay coefficients of variation were 6.6% and
7.8%, respectively.
Brain collection and analysis
On P40 and P90, 2 weeks following adult blood sampling,
rats were deeply anesthetized with a mixture of
Ketamine/Xylazine (40–80 mg/kg, i.p./5–10 mg/kg, i.p.)
and perfused intracardially with a phosphate-buffered
solution. Brains were quickly removed and placed over
ice. The prefrontal cortex and hippocampus were
immediately dissected, frozen on dry ice and stored at
�75 �C until processing.
Glutathione
Tissue concentrations of prefrontal cortex and
hippocampal glutathione were determined via a
fluorometric assay detection kit according to the
manufacturer’s instructions (ab65322, Abcam,
Cambridge MA, USA). Briefly, tissue was homogenized
458 M. MacRae et al. / Neuroscience 298 (2015) 455–466
and diluted 1:5. Samples were mixed with GST reagent
and monochlorobimane (supplied in kit) and incubated
at 37 �C for 1 h. The lower limit of detection was 1 nmol
and the assay to assay variability was within 5%.
Fluorescence was measured with excitation at 380 nm
and emission at 460 nm with a gain of 35.
Statistical analysis
All analyses were conducted using SPSS version 21.0
software. Passive maternal care behaviors (i.e.,
licking/grooming, nursing postures, total nursing
frequency, duration on nest) were evaluated using a
repeated measures design with ‘housing condition’ (SC,
EE) as the independent variable and observation day
(P3,P4,P5,P6) as the repeated variable. For the
remaining maternal behavior evaluations (i.e., overall
duration on nest, latency to start retrieval and open field)
one-way analysis of variances (ANOVAs) were employed
with housing condition as the independent factor. With
respect to neonatal treatment group comparisons (i.e.,
social behavior, object recognition test) we used three-
way ANOVAs with housing condition, ‘neonatal drug’
(nLPS, nsaline), and ‘sex’ (male, female) as the
independent factors. Plasma corticosterone, body weight,
and differences between young and adult glutathione
levels were similarly evaluated using a three-way
repeated measures ANOVA with time (corticosterone:
baseline, 15, 30, 60, and 120 min; body weight: P22–
P90; glutathione: P40 vs P90) as repeated factors. Area
under the curve for the corticosterone response was
evaluated using a three-way ANOVA, as above.
Greenhouse–Geisser corrections were applied to
violations to the assumption of sphericity. Significant
main effects were further assessed via pairwise t-tests
and Levene’s was applied in the occurrence of unequal
variances on the post hoc assessments. Bonferroni alpha
adjustments were applied as appropriate.
RESULTS
Maternal behavior
There were no significant housing, time, or housing by time
effects observed for the total number of pup retrievals,
licking/grooming, or nest building behaviors recorded
(p> 0.05; Fig. 2A shows total observations). Dams
reared in SC demonstrated more instances of low crouch
nursing (F(1,17) = 6.299, p= 0.023; Fig. 2B shows total
observations) however no other effects of nursing were
observed. There was a significant housing by time
interaction for the total duration of time spent on the nest
(F(3,51) = 3.069, p = 0.036; Fig. 2C). SC dams spent
more time on the nest on P5 (F(1,17) = 11.443,
p= 0.004) and P6 (1, 17) = 5.047, p= 0.038)
compared to EE dams. Overall there was no evidence of
passive maternal care variation as a function of neonatal
inflammation. With respect to the maternal preference
test, there was a significant three-way interaction
between housing condition, neonatal drug treatment, and
sex (F(1,44) = 4.618, p= 0.037; Fig. 2D). Follow-up
analyses with Bonferroni alpha corrections did not reveal
preferences for either sex or neonatal nLPS vs. nsaline
pups (p> 0.016). In the home cage retrieval task EE
dams had shorter latencies to begin (F(1,17) = 5.201,
p= 0.036; Fig. 2E) and fully (F(1,17) = 5.713,
p= 0.029; Fig. 2F) retrieve their litters compared to
standard housed rats. There were no neonatal treatment
differences in the latency of retrieval in the home cage
(p> 0.05; Fig. 2F). Based on the significantly decreased
latency for EE dams to retrieve their pups, we evaluated
maternal anxiety in an open field. There were no
differences in maternal housing conditions on percent of
entries into the center (p> 0.05; Fig. 2G) suggesting that
these animals were not anxious. Moreover, there were no
differences in body weights between nLPS and nsaline-
treated pups (p> 0.05) indicating that potential subtle
differences in maternal care did not affect this measure.
However, following application of the Greenhouse–
Geisser correction there was a significant interaction
between time and sex (F(2.736,150.453) = 114.753,
p= 0.0001) with male rats registering heavier than
females across time.
Social interaction
Juvenile social behavior was associated with a significant
neonatal treatment by housing interaction
(F(1,55) = 4.216, p= 0.045) in that nLPS-treated
animals spent a lower percentage of time in social
contact compared to their nsaline-treated standard
housed counterparts (t(29) = �2.084, p= 0.046;
Fig. 3A). There were no significant differences in either
the duration or frequency of initiating social engagement
(p> 0.05; Fig. 3B, C). However, there was significant
neonatal treatment by housing interactions with respect
to the duration (F(1,55) = 14.999, p= 0.0001) and
frequency (F(1,55) = 19.862, p= 0.0001) of social
behavior directed toward the rats by their conspecifics.
Specifically, SC nLPS-treated animals received lower
durations (t(29) = �2.600, p= 0.015; Fig. 3D) and
frequencies (t(29) = �3.063, p= 0.005; Fig. 3E) of
contacts directed toward them compared to SC-housed
nsaline rats. There were no differences between nLPS
and nsaline-treated rats housed in EE in terms of either
initiating or receiving contact (p> 0.05). Notably,
following Bonferroni alpha corrections, EE-housed
animals treated with nsaline had lower frequencies
(t(27) = �3.075, p= 0.005; Fig. 3E) but not durations
of contact initiated toward them compared to standard
housed controls.
A three-way ANOVA of adult social behavior showed
a main effect of drug on the frequency of contacts
initiated (F(1,56) = 4.735; p= 0.034). Follow-up tests
did not reveal any specific effects of drug on this
measure (p> 0.05, Fig. 3H). Total frequency receiving
contact revealed a significant interaction between sex
and housing condition (F(1,56) = 7.013, p= 0.010)
where male EE rats had fewer contacts initiated toward
them than standard housed rats (t(29) = �2.526,p= 0.017; Fig. 3J). There were no differences observed
on any other adult social measure (p> 0.05; Fig. 3F,
G, I). Therefore, nLPS rats show improvements in social
interactions across development.
Fig. 2. Maternal behavior. (A) Total frequency of pup retrieval, licking/grooming, and nest building across housing groups, (B) total frequency of
each nursing behavior (low, high, passive) and a combined score of all nursing behaviors, (C) total time (seconds) spent on the nest across all four
passive maternal observation days (P3, P4, P5, P6) and a combined total duration spent on the nest, (D)% pup preference in a novel context, (E)
latency to start pup retrieval and, (F) latency to retrieve the full litter in the home cage, (G) % of entries into the center of an open field (maternal
anxiety index). Rats were reared in either standard (SC) or environmentally enriched (EE) housing and offspring treated with neonatal (n)LPS or
nsaline; data are expressed as mean ± SEM; *p< 0.05, **p< 0.01.
M. MacRae et al. / Neuroscience 298 (2015) 455–466 459
Object-in-place
The three-way ANOVA for the juvenile discrimination ratio
revealed an effect of sex (F(1,58) = 4.786, p= 0.033)
but no effect of either neonatal treatment or housing
condition (p> 0.05; Fig. 4A). Post hoc follow up with
Levene’s confirmed a sex difference in that males had
higher discrimination ratios than females (t(56.373) =2.181, p= 0.033; Fig. 4A).
With respect to the adult discrimination ratio, a three-
way ANOVA uncovered an interaction between neonatal
treatment and sex (F(1,53) = 5.222, p= 0.026). Post
hoc follow up confirmed that adult male nLPS rats had
lower discrimination ratios compared to nsaline animals
(t(27) = �4.129, p= 0.0001; Fig. 4B). Overall, male
juvenile nLPS rats had an intact object-in-place memory
while their adult counterparts did not.
Plasma corticosterone response to a stressor
Evaluations of plasma corticosterone showed a significant
interaction between sex and time (F(1,39) = 16.594,
p= 0.0001) with females having significantly higher
levels of baseline (t(35.002) = �2.707, p= 0.010) and
Fig. 3. Social interaction data for male (left) and female (right) rats treated with neonatal (n)LPS or nsaline and reared in either standard (SC) or
environmentally enriched (EE) housing. Graphs illustrate (A, F) % of time in social contact, total (B, G) duration (seconds), and (C, H) frequency
initiating contact toward a novel conspecific, and total (D, I) duration (seconds) and (E, J) frequency receiving contact from a novel conspecific on
postnatal days 40 (top panel) and 70 (bottom panel), respectively. Mean ± SEM; ⁄p< 0.05, ⁄⁄p> 0.01.
460 M. MacRae et al. / Neuroscience 298 (2015) 455–466
Fig. 4. Object-in-place discrimination ratios for male (left) and female
(right) juvenile (top) and adult (bottom) rats following neonatal (n)LPS
or nsaline challenge. Animals were raised in standard (SC) or
environmentally enriched (EE) conditions. Mean ± SEM; *p< 0.05,**p> 0.01.
M. MacRae et al. / Neuroscience 298 (2015) 455–466 461
stress-induced corticosterone at 60 (t(30.921) = �4.607,p= 0.001) and 120 (t(39.689) = �2.547, p= 0.014)
minutes following restraint. There were no
consequences of neonatal treatment or housing
condition on either basal or stress-induced plasma
corticosterone. There was also a main effect of sex for
the area under the curve analysis with females having
higher levels than males (F(1,39) = 22.428, p= 0.0001).
Glutathione
ANOVA analysis for juvenile prefrontal cortex glutathione
level revealed a three-way interaction between neonatal
treatment, housing condition and sex (F(1,46) = 6.682,
p= 0.013). Male nLPS rats housed in standard
conditions had lower prefrontal glutathione levels than
nsaline-treated juveniles (t(12) = �2.406, p= 0.033,
Fig. 5A). There were no neonatal treatment differences
between juvenile males housed in EE (p> 0.05,
Fig. 5A) suggesting a protective effect of EE against
nLPS. Prefrontal glutathione level was higher in female
standard housed nLPS rats (t(12) = 4.010, p= 0.002,
Fig. 5A) and nsaline EE rats compared to nsaline SC
controls (t(8.965) = 2.863, p= 0.019, Fig. 5A), perhaps
indicative of a compensatory mechanism against
oxidative stress in females. There were no significant
neonatal treatment, housing or sex effects on adult
glutathione levels in the prefrontal cortex (p> 0.05,
Fig. 5B). With respect to juvenile hippocampal
glutathione levels, there was a two-way interaction
between housing condition and sex (F(1,46) = 11.759,
p= 0.001). Specifically, hippocampal glutathione levels
were augmented in female EE rats compared to their
SC counterparts (t(26) = 2.994, p= 0.006; Fig. 5C).
Adult hippocampal levels were significantly higher in
female rats compared to males (F(1,58) = 4.423,
p= 0.040); there was no additional neonatal treatment
or housing differences. Interestingly, a repeated
measures ANOVA (P40, P90) revealed that
hippocampal glutathione significantly increased across
all groups as animals matured (F(1,29) = 28.381;
p= 0.001; Fig. 5C, D), offering a potential explanation
for susceptibility to behavioral disruptions (i.e., social)
during the neonatal period following an inflammatory
triggering event.
DISCUSSION
The present work suggests that nLPS-induced
reprogramming is expressed in a time, sex, and
environmental context dependent manner. We
demonstrate that SC, but not EE, male and female rats
treated with a dual LPS protocol as neonates had
disrupted juvenile social interactions which were
remitted by maturity. In contrast, nLPS male animals
exhibited intact spatial memory as adolescents which
was impaired in later life. Moreover, SC nLPS males
had decreased prefrontal cortex levels of glutathione at
P40, which was normalized in adult animals. Overall,
these time-dependent effects provide additional
evidence that early-life inflammation interacts with other
developmental variables, specifically puberty
(Zuckerman et al., 2003; Meyer et al., 2006a) and EE,
in the expression (and prevention) of select behavioral
and molecular anomalies.
Considerations of environment
Since disruption of the nest and administration of LPS to
neonates may impact maternal care we evaluated several
behaviors to determine if dams treated their offspring
differently as a function of neonatal treatment and
housing. Although maternal licking and grooming (L/G)
is well recognized to have robust effects on offspring
development (Caldji et al., 1998; Kaffman and Meaney,
2007) we did not see changes on this measure in
response to our housing manipulation protocol. Instead,
we consistently show that EE dams spend less time on
the nest, which appears to differntially program later off-
spring anxiety-like behavior for novel vs. familiar environ-
ments (Connors et al., 2015). We also assessed whether
dams had preferences for particular offspring treatment
groups using maternal retrieval and preference tests. In
general, neonatal inflammation did not significantly depre-
ciate the value of pups by their mother. This suggests that
maternal care did not contribute to inflammatory-mediated
changes in the physiological and behavioral measures
evaluated here. However, we were surprised that there
was not a maternal preference for male vs. female pups,
as reported previously (Moore, 1985). Despite evidence
that MIA disrupts maternal care (Meyer et al., 2006b;
Penteado et al., 2014), in line with other observations
Fig. 5. Markers of oxidative stress in juvenile (left) and adult (right) offspring raised in standard (SC) or environmentally enriched (EE) housing
following neonatal (n)LPS or nsaline. Graphs depict glutathione levels expressed as nmol/mg in (A, B) prefrontal cortex and (C, D) hippocampus.*p< 0.05, **p> 0.01.
462 M. MacRae et al. / Neuroscience 298 (2015) 455–466
(Spencer et al., 2006; Bilbo et al., 2007), neonatal inflam-
mation in the present study did not alter dam behavior.
Interestingly, EE dams began retrieving their pups
sooner and gathered together the full litter more quickly
than standard housed rats. Based on the apparent
urgency of this responding we tested if they had
heightened levels of anxiety. Evaluations of the open
field test suggested that this was not the case. Previous
studies have shown that placement into EE in later life
reduces anxiety-like behavior in male rats (Pena et al.,
2009; Ravenelle et al., 2013), but we report no difference
compared to standard housed dams. Given the impact of
EE housing on maternal care, it is difficult to discern
between the contribution of these two variables, which
ought to be considered for all other measures of the study
when assessing the benefits of environmental
experience.
Our enriched environment appeared to offer some
protection against the early social deficits that followed
nLPS. Previously, EE has mitigated various animal
models of disease and trauma (Dahlqvist et al., 2004;
Spires et al., 2004; Johnson et al., 2013; Connors et al.,
2014), and increased social behavior (Morley-Fletcher
et al., 2003; Schneider et al., 2006) and preference direc-
ted toward animals reared in this condition (Mitra and
Sapolsky, 2012). Although EE seemed to prevent further
nLPS-induced reductions in social behavior, overall socia-
bility levels were lower in EE animals than we anticipated.
One major difference from past EE research is that our
animals received neonatal injections which may have
been interpreted as a stressor by the EE groups, affecting
behavior. Indeed, injection stress can impact experimen-
tal outcomes (Lapin, 1995; O’Callaghan et al., 2002)
and early-life stressors (i.e., maternal separation;
Morley-Fletcher et al., 2003; Holland et al., 2014) disrupt
social behavior.
Despite reported benefits of EE, particularly with
respect to cognition (van Praag et al., 2000), we did not
demonstrate protection against later-life spatial impair-
ments in nLPS males. Moreover, EE did not improve
the sustained inability of female rats to perform the
object-in-place discrimination task. Many EE studies are
confounded by the use of running wheels so the role of
physical activity vs. other elements of enrichment (i.e.,
social or novelty) cannot be clearly established.
Therefore we did not include running wheels in our
enriched housing. Given the benefits of hippocampal neu-
rogenesis as a consequence of wheel running (van Praag
et al., 1999), it is likely that the former environmental
manipulation would be more beneficial in the prevention
and rehabilitation of neuroinflammatory cognitive chal-
lenges, more so than enrichment alone. That said, EE
appeared to offer benefits against oxidative stress follow-
ing nLPS by preventing reduced glutathione levels in the
juvenile prefrontal cortex. An alternative interpretation is
that EE itself led to a reduction of glutathione in control
animals which may account for the lack of differences
between SC-nLPS and EE-nsaline juvenile males.
Given that our EE paradigm includes twice weekly toy
changes and varied social encounters it may be that our
animals interpreted these component(s) of their housing
as stressful. Indeed, chronic unpredictable mild stress is
known to reduce brain glutathione (Kumar et al., 2011).
However, there were no differences between SC-nsaline
and EE-nsaline/EE-nLPS glutathione levels in the juvenile
prefrontal cortex. Moreover, there were no indications of
M. MacRae et al. / Neuroscience 298 (2015) 455–466 463
dysregulation in resting plasma corticosterone or stress
recovery as a consequence of EE. Notably, others have
reported elevations in basal corticosterone and more effi-
cient stress recovery following 6 weeks of EE housing in
adulthood (Konkle et al., 2010). This is relevant because
our data suggest that enrichment protocols established
and maintained in early-life may not interfere with impor-
tant stress research endpoints. Indeed, evidence sug-
gests that environmental complexity may enhance
rather that diminish reproducibility in research, compared
to attempts at standardization across laboratories
(Richter et al., 2009).
Interestingly, juvenile EE females had elevated levels
of hippocampal glutathione compared to controls. This
effect was not sustained into adulthood, which may
confirm evidence that some EE benefits are more
enduring in males compared to females (Pena et al.,
2009). However, the observation that hippocampal glu-
tathione increased in both sexes across development
indicates that the effect was not lost in females but rather
protection from inflammatory-mediated oxidative stress
was conferred to both sexes across maturity.
Considerations of sex
Notably, lower social engagement following MIA in the
early-to-mid gestational period has been reported to
occur in a sex-specific manner with males but not
females being affected (Taylor et al., 2012; Connors
et al., 2014). However, in SC-housed rats, we demon-
strate reduced social contact in juveniles of both sexes
using the dual administration nLPS model. Autism, a neu-
rodevelopmental disorder associated with disrupted
social interactions, is reported four times more frequently
in males than females (CDC, 2014). Current hypotheses
posit that inflammation during early development may
be a factor involved in the etiology of this disorder
(Patterson, 2009). Given that in animal models the inutero effects are observed (or at least reported) most
often in males, it is possible that the underlying inflamma-
tory mechanism has a limited critical time period with
respect to its influence on females, accounting for the
lower incidence in this sex. Indeed, later MIA at P17
resulted in disrupted social interaction in both male and
female mice (Bitanihirewe et al., 2010) which we show
here using nLPs in rats. However, when relating the rele-
vance of these animal models to neurodevelopmental dis-
orders such as autism, further examination of sex
differences is warranted. This is evident given that
research and diagnostic practices often demonstrate a
sex bias toward males, potentially accounting for the
increased number of males reportedly affected (Lai
et al., 2015).
Prefrontal glutathione levels were higher in juvenile
female SC-nLPS rats compared to SC-nsaline controls
which may indicate a compensatory mechanism against
oxidative stress in females. It should be noted that
estrous cycles were not evaluated in these animals and
cyclic hormones could underlie some reported
differences. Additional work is necessary to determine
the role of reproductive hormones on glutathione-related
markers throughout the central and peripheral nervous
systems as findings have been inconsistent/difficult to
compare between humans and animal models (Browne
et al., 2008; Ozacmak and Sayan, 2009; Lee et al.,
2012; Priyanka et al., 2013; Mitra et al., 2015).
Considerations of time
Early-life inflammation is commonly associated with
spatial memory disruptions in a variety of behavioral
tasks (Dinel et al., 2014; Vorhees et al., 2015; Zhang
and van Praag, 2015). Moreover, studies demonstrate
the existence of ‘critical windows’ during which a chal-
lenge must take place in order for specific behavioral out-
comes to occur (Harre et al., 2008). Here, we confirm and
provide further evidence that these disruptions are also
mediated in a time-dependent manner with respect to
the trajectory of when they are expressed (i.e., adoles-
cence vs. adulthood). For example we show that juvenile
spatial memory is intact in male nLPS rats, but discrimina-
tion ability is compromised after maturity. Delays in cogni-
tive processes following early-life inflammation have been
reported previously. Specifically, MIA results in disrupted
latent inhibition in post-pubescent, but not juvenile, ani-
mals (Zuckerman et al., 2003; Meyer et al., 2006b).
Relatedly, Dinel et al. (2014) observed that P14 nLPS ele-
vated anxiety-like behavior in juvenile but not mature
mice, while the opposite time course was seen for
depressive-like symptoms in the forced swim test. We
extend upon these observations by reporting differential
expression of social disruptions between the juvenile
and adult periods of development. Furthermore, the pat-
tern of these social impairments was consistent with indi-
cators of oxidative stress in the prefrontal cortex of male
nLPS rats.
Our previous work suggests that overall decreased
social interaction following early-life inflammation is due
to reduced contact directed toward gestational and
neonatally treated LPS male rats (Connors et al., 2014;
MacRae et al., 2015). We show this here, but in both male
and female neonatally challenged animals. Notably, gen-
eral willingness to engage with a novel conspecific was
not disrupted, corresponding to previous reports (Ibi
et al., 2009). Specifically social behaviors initiated by
adult mice were not decreased following neonatal inflam-
mation – unless animals were repeatedly paired with the
same intruder, in which case they habituated more quickly
than controls (Ibi et al., 2009). However, the investigators
did not report the amount of contact directed toward the
neonatally treated animals. Still, these findings are in par-
allel with our data suggesting that (a) early-life inflamma-
tion may not necessarily decrease social interest directly
and/or (b) social impairments following neonatal exposure
are not as explicit in adulthood vs. the juvenile period.
Overall, this is interesting given that autistic individuals
are more likely to be rejected or overlooked by peers
and many express a desire for social interaction (Dean
et al., 2014). Moreover, some individuals reportedly show
improved emotional responsiveness, social reciprocity,
and socialization with age (McGovern and Sigman,
2005; Shattuck et al., 2007).
Together, these data consistently suggest a
programed timing in the emergence of impairments
464 M. MacRae et al. / Neuroscience 298 (2015) 455–466
following early-life inflammation in that (1) some
emotional disruptions are apparent by adolescence and
disappear post puberty while (2) maturity results in the
gradual unfolding of cognitive detriments. Since our
animals were housed under the same conditions (EE or
SC) between each juvenile and adult test point, it is
possible that puberty may be the contributing factor to
these outcomes. Future work must delineate the specific
hormones and other regulators underlying the trajectory
of affective, cognitive and associated molecular changes
in each specific inflammatory model (pre vs. postnatal).
CONCLUSIONS
With respect to early-life inflammation rarely do studies
simultaneously evaluate both juvenile and adult phases
of development, and very few investigate adolescent
development at all. Here, we demonstrate that nLPS-
induced reprogramming effects follow a sex and time-
dependent trajectory in terms of their expression.
Overall, this work extends upon the literature confirming
that early-life stress interacts with developmental
milestones (i.e., puberty) and the environment in the
expression (and prevention) of select behavioral and
molecular programs.
AUTHOR CONTRIBUTIONS
M.M., T.M., A.K., M.M.M., ran the experiments, M.M.M. &
A.C.K. analyzed data, M.M.M. & A.C.K. designed the
study and A.C.K. wrote the manuscript.
DISCLOSURES AND POTENTIAL CONFLICT OFINTERESTS
None.
Acknowledgments—We are grateful for the departmental support
provided by MCPHS University, the MCPHS Summer
Undergraduate Research Fellowship (SURF) awarded to M.M
and the Summer Healthcare Internship Program Grant awarded
to T.M.
REFERENCES
Bilbo SD, Newsum NJ, Sprunger DB, Watkins LR, Rudy JW, Maier
SF (2007) Differential effects of neonatal handling on early life
infection-induced alterations in cognition in adulthood. Brain
Behav Immun 21:332–342.
Bitanihirewe BKY, Peleg-Raibstein D, Mouttet F, Feldon J, Meyer U
(2010) Late prenatal immune activation in mice leads to
behavioral and neurochemical abnormalities relevant to the
negative symptoms of schizophrenia.
Neuropsychopharmacology 35:2462–2478.
Browne RW, Bloom MS, Schisterman EF, Hovey K, Trevisan M, Wu
C, Liu A, Wactawskiwende J (2008) Analytical and biological
variation of biomarkers of oxidative stress during the menstrual
cycle. Biomarkers 13:160–183.
Boksa P (2010) Effects of prenatal infection on brain development
and behavior: a review of findings from animal models. Brain
Behav Immun 24:881–897.
Caldji C, Tannenbaum B, Sharma S, Francis D, Plotsky PM, Meaney
MJ (1998) Maternal care during infancy regulates the
development of neural systems mediating the expression of
fearfulness in the rat. Proc Nat Acad Sci U S A 95:5335–5340.
Cechetti F, Worm PV, Lovatel G, Moyses F, Siqueira IR, Netto CA
(2012) Environmental enrichment prevents behavioral deficits and
oxidative stress caused by chronic cerebral hypoperfusion in the
rat. Life Sci 91:29–36.
Centers for Disease Control and Prevention (2014) Prevalence of
autism spectrum disorder—autism and developmental disability
monitoring network, 11 sites, United States, 2010. Surveill Summ
Mortal Wkly Rep 63:1–21.
Connors EJ, Shaik AN, Migliore MM, Kentner AC (2014)
Environmental enrichment mitigates the sex-specific effects of
gestational inflammation on social engagement and the
hypothalamic pituitary adrenal axis-feedback system. Brain
Behav Immun 42:178–190.
Connors EJ, Migliore MM, Shaik AN, Kentner AC (2015)
Environmental enrichment models a naturalistic form of
maternal separation and shapes the anxiety response patterns
of offspring. Psychoneuroendocrinology 52:153–167.
Coyle JT, Tsai G, Goff D (2003) Converging evidence of NMDA
receptor hypofunction in the pathophysiology of schizophrenia.
Ann N Y Acad Sci 1003:318–327.
Dahlqvist P, Ronnback A, Bergstrom SA, Soderstrom I, Olsson T
(2004) Environmental enrichment reverses learning impairment in
the Morris water maze after focal cerebral ischemia in rats. Eur J
Neurosci 19:2288–2298.
Dean M, Kasari C, Shih W, Frankel F, Whitney R, Landa R, et al.
(2014) The peer relationships of girls with ASD at school:
comparison to boys and girls with and without ASD. J Child
Psychol Psychiatry 55:1218–1225.
Dinel A-L, Joffre C, Trifilieff P, Aubert A, Foury A, Le Ruyet P, Laye S
(2014) Inflammation early in life is a vulnerable factor for
emotional behavior at adolescence and for lipopolysaccharide-
induced spatial memory and neurogenesis alterations at
adulthood. J Neuroinflammation 11:155.
Do KQ, Trabesinger AH, Kirsten-Kruger M, Lauer CJ, Dydak U, Hell
D, Holsboer F, Boesiger P, Cuenod M (2000) Schizophrenia:
glutathione deficit in cerebrospinal fluid and prefrontal cortex
in vivo. Eur J Neurosci 12:3721–3728.
Fan L-W, Tien L-T, Zheng B, Pang Y, Lin RCS, Simpson KL, Ma T,
Rhodes PG, Cai Z (2011) Dopaminergic neuronal injury in the
adult rat brain following neonatal exposure to lipopolysaccharide
and the silent neurotoxicity. Brain Behav Immun 25:286–297.
Forrest CM, Khalil OS, Pisa M, Smith RA, Darlington LG, Stone TW
(2012) Prenatal activation of toll-like receptors-3 by administration
of the viral mimetic poly(I:C) changes synaptic proteins, N-methyl-
D-aspartate receptors and neurogenesis markers in offspring. Mol
Brain 5:22.
Garay PA, Hsiao EY, Patterson PH, McAllister AK (2013) Maternal
immune activation causes age- and region-specific changes in
brain cytokines in offspring throughout development. Brain Behav
Immun 31:54–68.
Gu F, Chauhan V, Chauhan A (2015) Glutathione redox imbalance in
brain disorders. Curr Opin Clin Nutr Metab Care 18:89–95.
Harre E-M, Galic MA, Mouihate A, Noorbakhsh F, Pittman QJ (2008)
Neonatal inflammation produces selective behavioural deficits
and alters N-methyl-D-aspartate receptor subunit mRNA in the
adult rat brain. Eur J Neurosci 27:644–653.
Herring A, Lewejohann L, Panzer A-L, Donath A, Kroll O, Sachser N,
Paulus W, Keyvani K (2011) Preventative and therapeutic types
of environmental enrichment counteract beta amyloid pathology
by different molecular mechanisms. Neurobiol Dis 42:530–538.
Holland FH, Ganguly P, Potter DN, Chartoff EH, Brenhouse HC
(2014) Early life stress disrupts social behavior and prefrontal
cortex parvalbumin interneurons at an earlier time-point in
females than males. Neurosci Lett 566:131–136.
Ibi D, Nagai T, Kitahara Y, Mizoguchi H, Koike H, Shiraki A, Takuma
K, Kamei H, Noda Y, Nitta A, Nabeshima T, Yoneda Y, Yamada K
(2009) Neonatal polyI:C treatment in mice results in
schizophrenia-like behavioral and neurochemical abnormalities
in adulthood. Neurosci Res 64:297–305.
M. MacRae et al. / Neuroscience 298 (2015) 455–466 465
Johnson EM, Traver KL, Hoffman SW, Harrison CR, Herman JP
(2013) Environmental enrichment protects against functional
deficits caused by traumatic brain injury. Front Behav Neurosci
7:44.
Kaffman A, Meaney MJ (2007) Neurodevelopmental sequelae of
postnatal maternal care in rodents: clinical and research
implications of molecular insights. J Child Psychol Psychiatry
48:224–244.
Kempermann G, Gast D, Gage FH (2002) Neuroplasticity in old age:
sustained fivefold induction of hippocampal neurogenesis by long-
term environmental enrichment. Ann Neurol 52:135–143.
Khalil OS, Forrest CM, Pisar M, Smith RA, Darlington LG, Stone TW
(2013) Prenatal activation of maternal TLR3 receptors by viral-
mimetic poly(I:C) modifies GLUN2B expression in embryos and
sonic hedgehog in offspring in the absence of kynurenine pathway
activation. Immunopharmacol Immunotoxicol 35:581–593.
Konkle ATM, Kentner AC, Baker SL, Stewart A, Bielajew C (2010)
Environmental enrichment-related variations in behavioral,
biochemical, and physiologic responses of Sprague–Dawley and
Long Evans rats. J Am Assoc Lab Anim Sci 49:427–436.
Kumar B, Kuhad A, Chopra K (2011) Neuropsychopharmacological
effect of sesamol in unpredictable chronic mild stress model of
depression: behavioral and biochemical evidences.
Psychopharmacology 214:819–828.
Lai M, Lombardo MV, Auyeung B, Chakrabart B, Baron-Cohen S
(2015) Sex/gender differences in autism: setting the scene for
future research. J Am Acad Child Adolesc Psychiatry 54:11–24.
Lante F, Meunier J, Guiramand J, Maurice T, Cavalier M, de Jesus
Ferreira M-C, Aimar R, Cohen-Solal C, Vignes M, Barbanel G
(2007) Neurodevelopmental damage after prenatal infection: role
of oxidative stress in the fetal brain. Free Radical Biol Med
42:1231–1245.
Lapin IP (1995) Only controls: effects of handling, sham injection, and
intraperitoneal injection of saline on behavior of mice in an
elevated plus-maze. J Pharmacol Toxicol Methods 34:73–77.
Lee SY, Lee J-Y, Oh SJ, Kim HC, Kim SK (2012) Expression of
hepatic and ovarian antioxidant enzymes during estrous cycle in
rats. Toxicol Lett 3:329–336.
Liu Y-H, Lai W-S, Tsay H-J, Wang T-W, Yu J-Y (2013) Effects of
maternal immune activation on adult neurogenesis in the
subventricular zone-olfactory bulb pathway and olfactory
discrimination. Schizophr Res 151:1–11.
MacRae M, Kenkel WM, Kentner AC (2015) Social rejection following
neonatal inflammation is mediated by olfactory scent cues. Brain
Behav Immun. http://dx.doi.org/10.1016/j.bbi.2015.02.026. in
press.
McGovern CW, Sigman M (2005) Continuity and change from early
childhood to adolescence in autism. J Child Psychol Psychiatry
46:401–408.
Meyer U, Nyffeler M, Engler A, Urwyler A, Schedlowski M, Knuesel I,
Yee BK, Feldon J (2006a) The time of prenatal immune challenge
determines the specificity of inflammation-mediated brain and
behavioral pathology. J Neurosci 26:4752–4762.
Meyer U, Schwendener S, Feldon J, Yee BK (2006b) Prenatal and
postnatal maternal contributions in the infection model of
schizophrenia. Exp Brain Res 173:243–257.
Meyer U, Engler A, Weber L, Schedlowski M, Feldon J (2008a)
Preliminary evidence for a modulation of fetal dopaminergic
development by maternal immune activation during pregnancy.
Neuroscience 154:701–709.
Meyer U, Nyffeler M, Yee BK, Knuesel I, Feldon J (2008b) Adult brain
and behavioral pathological markers of prenatal immune
challenge during early/middle and later fetal development in
mice. Brain Behav Immun 22:469–486.
Mitra R, Sapolsky RM (2012) Short-term enrichment makes male rats
more attractive, more defensive and alters hypothalamic neurons.
PLoS One 7:e36092.
Mitra S, Chakrabarti N, Dutta SS, Ray S, Bhattacharya P, Sinha P,
Bhattacharyya A (2015) Gender-specific brain regional variation
of neurons, endogenous estrogen, neuroinflammation and glial
cells during rotenone-induced mouse model of Parkinson’s
disease. Neuroscience 292:46–70.
Moore CL (1985) Sex differences in urinary odors produced by young
laboratory rats (Rattus norvegicus). J Comp Psychol 99:336–341.
Morgan C, Novak I, Dale RC, Guzzetta A, Badawi N (2014) GAME
(Goals –Activity – Motor Enrichment): protocol of a single blind
randomized controlled trial of motor training, parent education and
environmental enrichment for infants at high risk of cerebral palsy.
BMC Neurol 14:203.
Morley-Fletcher S, Rea M, Maccari S, Laviola G (2003)
Environmental enrichment during adolescence reverses the
effects of prenatal stress on play behaviour and HPA axis
reactivity in rats. Eur J Neurosci 18:3367–3374.
O’Callaghan MJ, Croft AP, Little HJ (2002) Effects of intraperitoneal
injections of saline on the alcohol and sucrose consumption of
C57/BL10 mice. Psychopharmacology 160:206–212.
Ozacmak VH, Sayan H (2009) The effects of 17b estradiol and
progesterone on oxidative stress biomarkers in ovariectomized
female rat brain subjected to global cerebral ischemia. Physiol
Res 58:909–912.
Paintlia MK, Paintlia AS, Contreras M, Singh I, Singh A (2008)
Lipopolysaccharide-induced peroxisomal dysfunction
exacerbates cerebral white matter injury: attenuation by N-
acetylcystein. Exp Neurol 210:560–576.
Paris JJ, Brunton PJ, Russell JA, Frye CA (2011) Immune stress in
late pregnant rats decreases length of gestation and fecundity,
and alters later cognitive and affective behaviour of surviving pre-
adolescent offspring. Stress 14:652–664.
Patterson PH (2009) Immune involvement in schizophrenia and
autism: etiology, pathology, and animal models. Behav Brain Res
204:313–321.
Pena Y, Prunell M, Rotllant D, Armario A, Escorihuela RM (2009)
Enduring effects of environmental enrichment from weaning to
adulthood on pituitary-adrenal function, pre-pulse inhibition and
learning in male and female rats. Psychoneuroendocrinology
34:1390–1404.
Penteado SH, Teodorov E, Kirsten TB, Eluf BP, Reis-Silva TM,
Acenjo MK, de Melo RC, Suffredini IB, Bernardi MM (2014)
Prenatal lipopolysaccharide disrupts maternal behavior, reduces
nest odor preference in pups, and induces anxiety: studies of F1
and F2 generations. Eur J Pharmacol 738:342–351.
Priyanka HP, Sharma U, Gopinath S, Sharma V, Hima L,
ThyagaRajan S (2013) Menstrual cycle and reproductive aging
alters immune reactivity, NGF expression, antioxidant enzyme
activities, and intracellular signaling pathways in the peripheral
blood mononuclear cells of healthy women. Brain Behav Immun
32:131–143.
Raine A, Mellingen K, Liu J, Venables P, Mednick AA (2003) Effects
of environmental enrichment at ages 3–5 years on schizotypical
personality and antisocial behavior at ages 17 and 23 years. Am J
Psychiatry 160:1627–1635.
Ravenelle R, Byrnes EM, Byrnes JJ, McInnis C, Park JH, Donaldson
ST (2013) Environmental enrichment effects on the
neurobehavioral profile of selective outbred trait anxiety rats.
Behav Brain Res 252:49–57.
Richter SH, Garner JP, Wurbel H (2009) Environmental
standardization: cure or cause of poor reproducibility in animal
experiments? Nat Methods 6:257–261.
Schneider T, Turczak J, Przewłocki R (2006) Environmental
enrichment reverses behavioral alterations in rats prenatally
exposed to valproic acid: issues for a therapeutic approach in
autism. Neuropsychopharmacology 31(1):36–46.
Shattuck PT, Seltzer MM, Greenberg JS, Orsmond GI, Bolt D, Kring
S, Lounds J, Lord C (2007) Change in autism symptoms and
maladaptive behaviors in adolescence and adults with autism
spectrum disorder. J Autism Dev Disord 37:1735–1747.
Shi L, Fatemi SH, Sidwell RW, Patterson PH (2003) Maternal
influenza infection causes marked behavioral and
pharmacological changes in the offspring. J Neurosci
23:297–302.
466 M. MacRae et al. / Neuroscience 298 (2015) 455–466
Spencer SJ, Martin S, Mouihate A, Pittman QJ (2006) Early-life
immune challenge: defining a critical window for effects on adult
responses to immune challenge. Neuropsychopharmacology
31:1910–1918.
Spires TL, Grote HE, Varshney NK, Cordery PM, van Dellen A,
Blakemore C, Hannan AJ (2004) Environmental enrichment
rescues protein deficits in a mouse model of Huntington’s
disease, indicating a possible disease mechanism. J Neurosci
24:2270–2276.
Stolp HB, Johansson PA, Habgood MD, Dziegielewska KM,
Saunders NR, Ek CJ (2011) Effects of neonatal systemic
inflammation on blood–brain barrier permeability and behaviour
in juvenile and adult rats. Cardiovasc Psychiatry Neurol
469046:1–10.
Taylor PV, Veenema AH, Paul MJ, Bredewold R, Isaacs S, de Vries
GJ (2012) Sexually dimorphic effects of a prenatal immune
challenge on social play and vasopressin expression in juvenile
rats. Biol Sex Differ 3:15.
Van Praag H, Kempermann G, Gage FH (1999) Running wheel
increases cell proliferation and neurogenesis in the adult mouse
dentate gyrus. Nat Neurosci 2:266–270.
Van Praag H, Kempermann G, Gage FH (2000) Neural
consequences of environmental enrichment. Nat Rev Neurosci
1:191–198.
Vorhees CV, Graham DL, Braun AA, Schaefer TL, Skelton MR,
Richtand NM, Williams MT (2015) Prenatal immune challenge in
rats: effects of polyinosinic–polycytidylic acid on spatial learning,
prepulse inhibition, conditioned fear, and responses to MK-801
and amphetamine. Neurotoxicol Teratol 47:54–65.
Woo CC, Leon M (2013) Environmental enrichment as an effective
treatment for autism: a randomized controlled trial. Behav
Neurosci 127:487–497.
Zhang Z, van Praag H (2015) Maternal immune activation
differentially impacts mature and adult-born hippocampal
neurons in male mice. Brain Behav Immun 45:60–70.
Zuckerman L, Rehavi M, Nachman R, Weiner I (2003) Immune
activation during pregnancy in rats leads to a postpubertal
emergence of disrupted latent inhibition, dopaminergic
hyperfunction, and altered limbic morphology in the offspring: a
novel neurodevelopmental model of schizophrenia.
Neuropsychopharmacology 28:1778–1789.
(Accepted 21 April 2015)(Available online 29 April 2015)