PRENATAL AND PERINATAL CANNABINOID EXPOSURE
First, we will briefly summarize the results of human studies that investigated the consequences of developmental exposure to cannabinoids on cognitive performance, and then we will focus on rodent studies.
Since the late 1970s, two extended longitudinal cohort studies, the Ottawa Prenatal Prospective Study (OPPS) and the Maternal Health Practices and Child Development Study (MHPCD), have been measuring the cognitive functions of children born from mothers who consumed
Cannabis sativa preparations during pregnancy (
Day et al., 1992;
Fried, 2002b;
Trezza et al., 2008b;
Campolongo et al., 2009c,
2010). These studies showed that the consequences of prenatal exposure to cannabis are rather subtle. Immediately after birth, there is little evidence for a prenatal cannabis effect either upon growth or behavior (
Fried and Watkinson, 1988). However, beyond the age of 3, there are findings suggesting an association between prenatal cannabis exposure and aspects of cognitive behavior that fall in the domain of executive functions (
Fried and Watkinson, 1990;
Day et al., 1992,
1994;
Fried et al., 1998;
Fried and Smith, 2001;
Fried, 2002b;
Trezza et al., 2008b). Executive functions refer to higher-order cognitive functions such as cognitive flexibility, sustained and focused attention, planning and working memory. These functions enable us to organize and manage the many tasks in our daily life; for instance, to account for short- and long-term consequences of our actions, to make real time evaluations of our actions, and make necessary adjustments if these actions are not achieving the desired results. Impairments in executive functions have a major impact on our ability to perform tasks as planning, prioritizing, organizing, paying attention to and remembering details, and controlling our emotional reactions. In particular, the facets of executive functions which appear to be affected by cannabis exposure are the domains of attention/impulsivity and problem solving situations requiring integration and manipulation of basic visuoperceptual skills (
Fried and Watkinson, 1990;
Day et al., 1992,
1994;
Fried et al., 1998;
Fried and Smith, 2001;
Fried, 2002b;
Trezza et al., 2008b). The deficits in executive functions induced by prenatal cannabis exposure seem to be long-lasting, since 18- to 22-year-old young adults exposed to cannabis during pregnancy showed altered neuronal functioning during visuospatial working memory processing (
Smith et al., 2006).
Although there is a convergence of evidence in human studies, the very limited number of studies which have followed children beyond the age of 3 emphasizes the need for further, well-controlled investigations in this area. Furthermore, it cannot be excluded from human studies that genetic and environmental variables also contribute to the relationship between maternal cannabis use and long-term cognitive deficits in the offspring. Therefore, the long-term effects of prenatal exposure to cannabinoid drugs on cognitive functions in rodents have received a great deal of attention. Prenatal exposure to a moderate dose of the synthetic CB
1 cannabinoid receptor agonist WIN55,212-2 (0.5 mg/kg from GD 5 to GD 20) has been shown to induce a disruption of memory retention in 40- and 80-day-old rat offspring tested in the inhibitory avoidance task (
Mereu et al., 2003). This cognitive impairment was not due to alterations of non-associative nature, since the approach latency during the acquisition trials of the task was unaffected. The memory impairment in WIN55,212-2-exposed offspring was associated with alterations in hippocampal long-term potentiation (
Mereu et al., 2003).
In vivo microdialysis experiments also showed a significant decrease in basal and K
+-evoked extracellular glutamate levels in the hippocampus of juvenile and adult rats born from WIN55,212-2-treated dams (
Mereu et al., 2003). The decrease in hippocampal glutamate overflow was suggested to be the cause of disrupted long-term potentiation, which could, in turn, underlie the long-lasting memory impairment caused by gestational exposure to the cannabinoid receptor agonist (Mereu et al., 2003). To further support the hypothesis that changes in glutamatergic neurotransmission might be responsible of the cognitive impairment observed in WIN55,212-2-exposed offspring,
in vivo microdialysis experiments showed that basal and K
+-evoked glutamate levels were significantly lower in the cerebral cortex of both adult (90-day-old) and adolescent (40-day-old) rats exposed to WIN55,212-2 during gestation than in those born from vehicle-treated mothers (
Antonelli et al., 2004;
Castaldo et al., 2007;
Ferraro et al., 2009). Interestingly, the cognitive deficits induced by prenatal exposure to WIN55, 212-2 appeared already at early developmental ages. Thus, 10- to 12-day-old WIN55,212-2-exposed pups showed a poorer performance in homing behavior, a simple form of learning occurring during the early phases of postnatal life (
Antonelli et al., 2005). At the neurochemical level, basal and K
+-evoked glutamate levels were significantly lower in primary cell cultures of hippocampus (Mereu et al., 2003) and cerebral cortex (
Antonelli et al., 2005,
2006) obtained from pups exposed to WIN55, 212-2 compared to pups from the control group. The alteration of cortical glutamate transmission induced by prenatal WIN55,212-2 exposure was also associated with a significant reduction of NMDA receptor-mediated regulation of glutamate levels (
Ferraro et al., 2009). In fact, the NMDA-induced concentration-dependent increase of glutamate levels observed in cortical cell cultures obtained from neonates born from vehicle-treated dams was completely lost in cell cultures obtained from pups prenatally exposed to WIN55,212-2 (
Antonelli et al., 2005). These results suggest that chronic prenatal treatment with WIN55, 212-2 induces a loss of NMDA receptor activity in the exposed offspring (
Antonelli et al., 2005;
Ferraro et al., 2009).
Morphological experiments have shown that prenatal exposure to WIN55,212-2 also affects neuronal proliferation: a different neurite growth pattern was observed in cortical cell cultures obtained from pups born from mothers exposed to WIN55,212-2 during pregnancy (
Antonelli et al., 2005;
Ferraro et al., 2009). Cortical cell cultures from vehicle-exposed pups showed a high number of healthy neurons, which developed in a monolayer to form a complex network of neurites. On the contrary, cortical cultures obtained from pups exposed to WIN55,212-2 during pregnancy showed a minor population of neurons and abnormal neurite outgrowth, characterized by impairments of neurite branching (
Antonelli et al., 2005;
Ferraro et al., 2009).
Exposure to cannabinoid agonists during critical periods of brain development is known to cause long-term changes in the functionality of several neurotransmitter systems in adulthood, such as alterations in dopaminergic (
Rodriguez de Fonseca et al., 1991;
Bonnin et al., 1994,
1995), opioidergic (
Vela et al., 1995,
1998), serotonergic (
Molina-Holgado et al., 1996), and GABAergic (
Garcia-Gil et al., 1999a) systems. In addition, prenatal exposure to WIN55,212-2 has been found to induce long-term changes in the activity of the endocannabinoid system: in particular, the functionality of CB
1 receptors in the hippocampus differed between adult WIN55, 212-2- and vehicle-exposed offspring (
Castelli et al., 2007). Thus, it can be speculated on basis of the
in vitro and
in vivo results that gestational WIN55, 212-2-exposure produces enduring alterations of the endocannabinoid system in the developing brain, which may lead to a long-lasting and irreversible disruption of glutamate cortical and hippocampal function (
Castelli et al., 2007;
Ferraro et al., 2009).
As for the clinical relevance of these preclinical studies, it is important to estimate, by extrapolation, whether the dose of the synthetic cannabinoid agonist WIN55,212-2 is comparable to that of the main active ingredient of cannabis, Δ9-tetrahydrocannabinol (THC), absorbed by cannabis users. It has been estimated that a dose of 5 mg/kg of THC in rats corresponds to a moderate exposure to the drug in humans, correcting for the differences in route of administration and body weight surface area (
Garcia-Gil et al., 1997,
1999a,
b). WIN55,212-2 has been found to be 3-10 times more potent than THC, depending on the administration route and the behavioral endpoints considered (
Compton et al., 1992;
French et al., 1997;
Hampson et al., 2000). This mirrors the CB1 receptor affinity rank order for the two drugs (
Matsuda, 1997;
Pertwee, 1997). Based on these considerations, the dose of WIN55,212-2 used in the studies described above corresponds to a moderate, or even to a low, exposure to cannabis in humans (
Mereu et al., 2003). Furthermore, in line with studies that used a protocol of prenatal WIN55,212-2 exposure, it has been demonstrated that the active ingredient of cannabis, THC, administered during the perinatal period at a dose (5 mg/kg, per os, from GD 15 to PND 9) that is not associated with gross malformations and/or overt signs of toxicity, induces cognitive impairments in the adult offspring (
Campolongo et al., 2007). Importantly, perinatal exposure to THC not only induced a long-term memory impairment in the adult offspring, as revealed by the inhibitory avoidance test, but also a disruption in short-term olfactory memory, as assessed in the social discrimination test (
Campolongo et al., 2007). This form of memory, that plays a crucial role in the processing of social information, requires integral glutamatergic projections from the hippocampal formation to prefrontal areas (
Steckler et al., 1998;
McGaugh, 2002), and then back from the prefrontal cortex to the hippocampus. Interestingly, the cognitive impairments observed in THC-exposed adult offspring were associated with long-lasting alterations in the cortical expression of genes related to glutamatergic neurotransmission, together with a decrease in the cortical extracellular levels of this neurotransmitter (
Campolongo et al., 2007). Furthermore, in line with studies that used a protocol of prenatal WIN55,212-2 exposure, the neurochemical changes induced by prenatal THC exposure appeared early in development, as altered regulation of glutamate release and decreased functional activity and expression of GLT1 and GLAST glutamate transporters in the hippocampus of adolescent rats perinatally exposed to THC have been reported (
Castaldo et al., 2010). Again, these studies strongly suggest that changes in glutamatergic neurotransmission might be responsible for the cognitive deficits induced by prenatal cannabinoid exposure.
ADOLESCENT CANNABINOID EXPOSURE
In most Western Countries, the first episodes of cannabis use often occur during adolescence (
NIDA, 2005;
Hall and Degenhardt, 2009;
SAMHSA, 2009). Adolescence is a critical phase for CNS development during the transition from childhood to adulthood (
Spear, 2000;
Andersen, 2003). It is a period characterized by widespread neuronal plasticity and maturation at the neural and network level, when the brain undergoes both progressive and regressive changes including extensive synaptic remodeling and pruning and alterations in neurotransmitter levels and their receptors in cortical and limbic brain regions across different species (
Spear, 2000;
Andersen, 2003), processes in which the endocannabinoid system plays a major role (
Spear, 2000;
Andersen, 2003;
Freund et al., 2003;
Bossong and Niesink, 2011;
Rubino et al., 2011).
Both neuropsychological and functional imaging studies indicate that the detrimental effects of cannabis on cognitive performance may be more pronounced when cannabis is used during adolescence (
Ehrenreich et al., 1999;
Jager and Ramsey, 2008;
Schweinsburg et al., 2008;
Bossong and Niesink, 2011). Most imaging studies in adolescent subjects reported cannabis-induced alterations in working memory (
Jacobsen et al., 2004,
2007;
Schweinsburg et al., 2008). Studies making a distinction between the initiation of cannabis use in adolescence and in adult life showed attention deficits and poor cognitive performance in early-onset cannabis users (onset before age 17), but not in late-onset users or control subjects (
Ehrenreich et al., 1999;
Pope Jr. et al., 2003).
Quinn et al. (2008) showed that adolescent but not adult rats displayed significantly impaired object recognition memory and altered protein expression profiles in the hippocampus following repeated THC exposure. Similarly,
Schneider and Koch (2003) showed that chronic pubertal treatment with WIN55,212-2 resulted in impaired object recognition memory in adulthood, associated with disrupted prepulse inhibition of the acoustic startle response and lower break points in a progressive-ratio operant behavioral task (
Schneider and Koch, 2003). Again, it is worth noting that if the chronic cannabinoid treatment was administered during adulthood, none of the tested behaviors was affected (
Schneider and Koch, 2003). Gender-specific effects of chronic adolescent cannabinoid exposure have also been reported (
O’Shea et al., 2004,
2006). In these studies, the cannabinoid receptor agonist CP-55,940 was administered daily for 21 consecutive days to either adolescent or adult male and female rats. Following a long drug-free period, working memory was assessed in the object recognition task (
O’Shea et al., 2004,
2006). In females, cannabinoid-treated adolescent, but not adult rats demonstrated impaired working memory compared to vehicle-treated controls (
O’Shea et al., 2004,
2006). Interestingly, in males, cannabinoid treatment during adolescence and adulthood produced similar working memory deficits (
O’Shea et al., 2004). Thus, in females, adolescents may be more susceptible and adults more resilient to long-lasting cannabinoid-induced cognitive deficits, whereas in males, both adolescents and adults are equally vulnerable. Deficits in object recognition memory have also been reported in adult female rats treated chronically with THC during adolescence (
Realini et al., 2011).
Developmental and gender sensitivity to cannabinoid compounds has been further investigated by
Cha et al. (2006,
2007), who assessed spatial memory in the Morris water maze task following acute and chronic THC exposure in male and female adolescent and adult rats. Acute THC exposure led to greater learning impairments in adolescent than in adult male and female rats tested in both the spatial and non-spatial versions of the water maze tasks (
Cha et al., 2006,
2007). Conversely, chronic THC administration during either adolescence or adulthood had no effect on spatial learning in animals of both sexes tested after a long drug-free period (
Cha et al., 2006,
2007). Thus, while adolescents may be more sensitive to the acute effects of cannabinoids, both adolescents and adults demonstrated similar recovery of cognitive performance following discontinuation of chronic treatment (
Cha et al., 2006,
2007). In line with these findings, it has been reported that adolescent exposure to the cannabinoid receptor agonist CP-55,940 did not affect adult performance of animals of both sexes in the water maze task (
Higuera-Matas et al., 2009). However, following adolescent exposure to THC, spatial working memory in the radial maze task was impaired in both male and female adult rats, while aversive memory in the inhibitory avoidance task was unaffected (
Rubino et al., 2009a,
b). The neural underpinnings of the spatial working memory impairments observed in the latter studies may differ between males and females (
Rubino and Parolaro, 2011). Indeed, adult female rats showed reduced levels of proteins involved in synaptic plasticity and altered pattern of protein expression in synaptosomes from prefrontal cortex, with no alterations in the hippocampus (
Rubino et al., 2009a). Conversely, in adult male rats pre-exposed to THC during adolescence, the spatial working memory deficit was related to reduced levels of markers of neuroplasticity and morphological alterations in the hippocampus (
Rubino et al., 2009b). These results suggest that the same protocol of adolescent THC exposure, although resulting in similar behavioral endpoints, may have different neuronal consequences in the brain of male or female rats.
Long-term sexually dimorphic effects induced by adolescent THC exposure on cognitive performance have also been described by
Harte and Dow-Edwards (2010), who examined the effects of adolescent THC exposure on visual spatial learning in adulthood using the active place avoidance test. This cognitive task allows to simultaneously assess the ability to learn and retrieve spatial information, as well as flexibility of learning, by training animals to actively move over a slowly rotating arena and avoid an unmarked sector, entering which is punished by a mild footshock. The shock sector is defined in a stable position with respect to the experimental room. Animals must thus localize the shock sector exclusively by its spatial relations to distal orienting cues located in the room and walk into the safe part of the arena in a direction opposite to arena rotation (
Cimadevilla et al., 2000). By using this task,
Harte and Dow-Edwards (2010) showed that THC administration during early adolescence had no effect on the acquisition of the task. However, male and female animals treated with THC during early adolescence made more errors on the reversal trial requiring flexibility in learning. Conversely, THC administration during late adolescence had no effect in both sexes. Therefore, early adolescence appeared to be more sensitive to the cognitive effects of THC than late adolescence (Harte and Dow-Edwards, 2010). These findings indicate that the time window during adolescence in which THC is administered can have a profound influence on its long-lasting cognitive outcomes.