THE EFFECTS OF PRENATAL LEAD EXPOSURE ON THE DEVELOPMENT OF BIOMARKERS OF ALZHEIMER’S DISEASE by Andrew Wood A Senior Honors Project Presented to the Honors College East Carolina University In Partial Fulfillment of the Requirements for Graduation with Honors by Andrew Wood Greenville, NC May 2015 Approved by: Jamie C. DeWitt Department of Pharmacology and Toxicology Brody School of Medicine ABSTRACT - While often well known for its adverse effects on memory, Alzheimer’s disease (AD) is also noteworthy for being the sixth leading cause of death in the United States. An estimated 5.2 million Americans had the disease as of 2013, with the number of cases expected to increase in coming decades. Research into the condition has not revealed its exact cause; however, AD is believed to result from a combination of genetic vulnerabilities and environmental influences. An important aspect of AD and this study is the development of plaques or clumps of amyloid beta (AΒ) protein in the brains of those with AD, with increased concentrations of AΒ indicating a more severe condition. Microglia, resident immune cells of the brain, are thought to influence the level of these proteins in the brain. Prenatal exposure to environmental contaminants may influence the actions of microglia during an organism’s lifetime in a way that encourages the development of AD and its observable plaques. This study explored both the separate and combined effects of environmental agents and genetic predispositions to the disease. This was done by exposing both 3x-Tg-AD mice, that have a genetic predisposition to developing AD, and wild-type mice to lead prenatally. The level of AΒ42 in brains was measured by ELISA at varying ages, and the differences in AΒ-42 was compared between wild-type and transgenic animals between doses for each age and each sex. The final results showed a significant increase in AB-42 concentration in fully mature 3x-Tg-AD mice that were exposed to lead. This evidence supports our hypothesis that developmental exposure to an exogenous contaminant prenatally would exacerbate the tendency of genetically vulnerable organisms to develop the pathologies of AD. 1 Table of Contents Introduction 3 The Pathologies of Alzheimer’s Disease 3 The Role of Microglia in Alzheimer’s Disease 3 Critical Window of Development 5 Hypothesis 5 Relevance 5 Methods 7 Animals and Dosing 7 AB Levels 8 Statistical Analysis 9 Results 9 Discussion 14 Literature Cited 16 2 Introduction The Pathologies of Alzheimer’s Disease Alzheimer’s disease (AD) is the most common cause of dementia, a condition in which the patient experiences behavioral abnormalities and a loss of cognitive functioning (U.S. Department of Health and Human Services [USDHHS], 2011). While these mental effects are well known symptoms of AD, those with the disease also show physical abnormalities within the brain itself. The first of these biological markers of AD is the formation of neurofibrillary tangles within the neurons of the brain (USDHHS, 2011). These tangles are due to an accumulation of abnormal tau protein. While this protein typically supports the inner transport system of neurons, the brains of AD patients show a large number of these proteins breaking away from their normal position and clumping together to form tangles (U.S. Department of Health and Human Services [USDHHS], 2013-2014). The second major neuropathological biomarker of AD is the abnormal accumulation of amyloid beta (AΒ) protein plaques within the brain. Small clumps of AB along with the larger accumulated plaques may interfere with the ability of neurons to function and communicate properly. A buildup of tangles and plaques can result in the death of large numbers of neurons, eventually resulting in the loss of cognitive function that is characteristic of patients with AD (USDHHS, 2013-2014). These biomarkers can also be used to confirm the presence and extent of AD in a patient after death (USDHHS, 20132014). The Role of Microglia in Alzheimer’s Disease Microglia cells are the resident immune cells of the brain. Their normal functions include directing the actions of the immune system locally and, when necessary, phagocytizing 3 damaged or dead cells and cellular debris (Solito & Sastre, 2012). These actions are important to maintain the normal brain environment. However, there is also evidence that the microglial response to inflammation can actually harm neurons. As an individual ages, microglia become less efficient in function, becoming over-activated when stimulated and producing too harsh a reaction to stimulation (Solito & Sastre, 2012). Such prolonged responses of inflammation are detrimental to neurons and could exacerbate or even lead to an environment that culminates in AD. Microglia therefore are thought to have positive and negative effects on the development of AD. Microglia are being mentioned here because of the relationship that they are thought to have with amyloid beta proteins. The “macrophage” role of microglia would typically include the removal of excess AB protein found within the brain of a patient with AD (Solito & Sastre, 2012). Accumulating evidence therefore suggests that the existence of AB plaques in AD patients indicates some sort of error in microglia function that either limits phagocytosis of AB or increases deposition of AB. Increased AB levels have then been shown to start a vicious “feed-forward cycle” with microglia cells. These unnaturally high levels of AB are thought to activate microglia to increase local inflammation of immune system activity (Solito & Sastre, 2012). This increased inflammation may affect the transcription of the enzyme responsible for AB generation, β-secretase (Solito & Sastre, 2012). While the exact role of microglia in the brain of a patient with AD is not fully known, it is generally agreed upon that they play an important role in the disease. While this part of the project does not specifically address microglia, they are being assessed as part of the larger project. However, it is important to consider the role that they might play in AB deposition and/or clearance. 4 Critical Window of Development While changes in the immune and nervous systems occur naturally as an organism ages, changes may also occur due to events that occur early in life. Microglia have been shown to be sensitive to pre-natal exposure to exogenous contaminants (Diz-Chaves, Pernía, Carrero, & Garcia-Segura, 2012). Exposure to such contaminants during a “critical window” of microglia development could alter microglia in a way that increases the potential of neurodegenerative disorders, such as AD. Hypothesis Our overall hypothesis is that early-life exposure to an exogenous stimulus, such as an environmental chemical, reprograms microglia and changes their responsiveness to other signals, leading to early onset and/or increased severity of AD pathologies. For this portion of the project, changes in levels of AB in wild-type and transgenic 3xTgAD mice after prenatal exposure to lead will be evaluated. These transgenic mice have multiple mutations, one of which increases their potential to develop amyloid beta plaques within the brain as they age. Relevance AD is not a single origin disease. It is thought to occur due to a combination of both genetic and environmental factors (USDHHS, 2013-2014). The novelty of this study is the idea of a “double hit” model that compares and contrasts the effects of both of these origins. This “double hit” is accomplished by using both transgenic mice to observe genetic effects (hit 1) and lead exposure to observe the effect of environmental influences (hit 2) on the development of the biomarkers for AD. A second important facet of this study is the link between pre-natal exposures to exogenous contaminants and diseases seen later in life. While many studies have 5 shown a positive correlation between these events, ours will investigate the “how” behind this correlation by observing the contaminant’s effect on the form and function of microglia, and the resultant effect on AB levels. Understanding the mechanisms behind AD development would be very helpful when attempting to design prevention and treatment strategies that focus on the developmental process. 6 Methods Animals and Dosing The study involved two separate strains of mice, the 3xTgAD transgenic mice and the associated wild-type. The transgenic mice are genetically predisposed to developing behavioral abnormalities, neurofibrillary tangles, and AB plaques. Two female mice of each strain were paired with the appropriate males (transgenic females with transgenic males, and wild-type females with wild-type males) overnight each week. The day after each pairing was designated gestational day one (GD1). Females were then assigned to either a treated or a control group and were then gavaged with 100 mg/kg (as 0.1 uL/10 g of body weight) of lead acetate or a vehicle control from gestational days 7-11. This period of development was chosen as it is one of several critical periods for microglial development/migration. Litters were culled at postnatal day (PND) five, to three male and three female pups when possible. Pups were weaned at PND21 and were sorted into same-sex sibling trios when possible; single housing also was avoided when possible. Adult offspring were culled at PND 50, 90, and 180. The PND50 samples served as controls for AB levels and as a time point for very early onset of neuropathologies. The PND180 samples represented an age when the transgenic mice should show signs of neuropathologies. The PND90 samples were an “in-between” age for early onset of neuropathologies. 7 AB Levels Brains were immediately removed upon euthanasia and separated into specific sections. The right and left hemispheres of the brain were separated and the hippocampus of the left hemisphere was removed. The right hemisphere with hippocampus intact was snap frozen on dry ice and kept frozen at -80°C until analysis. This portion of the brain was gently homogenized using glass homogenizers and a homogenization buffer that included a protease inhibitor. This solution was then mixed with a saline solution containing diethylamine and homogenized again. The resulting liquid mixture was run on a centrifuge for 1 hour at 14,000 rpm. The homogenate was then extracted and frozen at -80°C. The right half of each brain was analyzed for AB-42 by enzyme linked immunosorbent assay (ELISA). The assays were performed using Colorimetric BetaMark Beta-Amyloid x-42 ELISA kits. The protocol for these kits involved adding diluted samples and a standard solution to a 96 well plate coated with an antigen specific to this assay. The standard solution was used to create sequentially diluted solutions that varied from 0 to 250 pg/mL final concentrations. The standards were allotted to two columns of the plate, leaving 80 wells in which samples were run in singlets or duplicates. A detection antibody was then added to all wells before the plate was placed in a 4°C fridge to incubate overnight. After incubation, the plate was washed to remove excess antibodies from solution. A TMB solution was then added to all wells to start a reaction that would “color” each well based on the amount of AB-42 each sample contained. After a short incubation period, the plates were analyzed at 620nm using a microplate reader. The absorbance of each sample was converted to the AB-42 concentration from the data given by the standard curve. 8 Statistical Analysis Data were evaluated with pairwise comparisons (t-tests) within age and within sex. Comparisons within age and sex included mean differences in AB-42 concentration between control and treated wild-type animals, control and treated transgenic animals, control wild-type and transgenic animals, and treated wild-type and transgenic animals. Differences across age and between sexes were not evaluated for this aspect of the study. Results At PND50, transgenic male animals treated with lead acetate had approximately 20% higher AB-42 levels relative to control transgenic male animals (Figure 1). All other groups differed by about 15% or less at this age. In brains of animals collected at PND90, levels of AB-42 in brains of all control animals were equal to or greater than levels of AB-42 in brains of all treated animals (Figure 2). However, this difference was only statistically significant in the female wildtype animals. When evaluated at PND180 (Figure 3), levels of AB-42 in brains of wild-type animals were relatively equal between control and treated animals (differed by less than 15%, on average). In the transgenic animals, however, levels of AB-42 in treated female animals was nearly 60% greater relative to control animals and in treated male animals, was 87% greater relative to control animals. The variability in the results for the male animals prevented this difference from being statistically significant. At postnatal days (PND) 50 and 90, levels of AB-42 did not differ appreciably between control and treated animals or between wild-type and transgenic animals (Figure 4). 9 Figure 1: Mean AB-42 concentration (pg/mL) among animals collected at postnatal day 50. AB42 from the transgenic (Psen) males treated with lead acetate was elevated relative to the control Psen males (*). 10 Figure 2: Mean AB-42 concentration (pg/mL) among animals collected at postnatal day 90. AB42 from the wild-type females treated with lead acetate was reduced relative to the control wild-type females (*). 11 Figure 3: Mean AB-42 concentration (pg/mL) among animals collected at postnatal day 180. AB42 from the transgenic (Psen) females treated with lead acetate was elevated relative to the control Psen females (*). 12 A B Figure 4: Mean AB-42 concentration (pg/mL) among animals collected at postnatal day 50, 90, and 180. A) Males. B) Females. 13 Discussion Our hypothesis for this experiment was that early-life exposure to an exogenous stimulus, such as an environmental chemical, reprograms microglia and changes their responsiveness to other signals, leading to early onset and/or increased severity of AD neuropathologies. While the role (or lack thereof) of microglia in this particular facet of the experiment was not evaluated, the results do support our hypothesis of increased presence of AD neuropathologies, as indicated by increased AB-42 levels, after a prenatal exogenous stimulus. In the PND 180 groups, the treated transgenic mice had a large increase in AB-42 concentration over the control transgenic mice. While prenatal exposure to lead did not increase the average concentration of AB-42 in wild-type mice, it did exacerbate the tendencies of transgenic mice to develop this observed neuropathology. One result that we did not observe in this experiment was an early-onset increase in AB-42 concentration. Control transgenic animals had increased AB-42 at PND180 relative to the wild-type animals, but treated wild-type animals did not have increased AB-42 at any time point. A similar experiment measured the expression of the APP gene (which produces the precursors of AB) in rats exposed to lead early in life and in a separate group of rats exposed to lead in old age. Early life lead exposure was found to increase APP expression late in life; however, exposure to lead late in life did not result in a similar increase in expression (Basha, Wei, Bakheet, Benitez,Siddiqi, Ge, Lahiri, & Zawia 2005). These observations are in agreement with our findings of increased AB expression late in life. As treated transgenic animals did not have increases in AB-42 at either PND50 or PND90 (Figure 4), this suggests that some critical event occurs in the treated transgenic animals that is not occurring in the treated wild-type animals. While additional work is ongoing in our laboratory to understand why this is 14 occurring, we hypothesize that the microglia in the treated transgenic animals are hypo- or hypersensitive to the altered neuronal microenvironment induced by the mutations. Some of our conclusions were confounded by the high variability of our results. While the increased variability could have been caused by a number of factors, it was likely due to pipetting error or malfunction causing an uneven amount of sample to be put in each sample well. Extra care should be taken during this critical step of pipetting samples into their respective wells, and any user should test pipette precision and accuracy before starting procedures. This variability could also possibly be caused by denaturation of AB during the homogenization procedure. Ethanol was used to clean homogenizers, and users should ensure the glassware is completely dry before processing samples. The real world application of these results will be to help formulate ideas and future studies on the origins of AD. Our results support the idea that exposure to immunotoxicants during early development can increase the probability of genetically predisposed individuals to developing AD in the future. However, increased AB levels are only one aspect of AD development. Further research would be needed to see if there is actual evidence of mental impairment or neuronal damage as a result of a prenatal toxicant exposure. 15 Literature Cited Basha, R. M., Wei, W., Bakheet, S. A., Benitez, N., Siddiqi, H. K., Ge, Y.-W, Lahiri, D.K., & Zawia, N. H. (2005). The fetal basis of amyloidogenesis: Exposure to lead and latent overexpression of amyloid precursor protein and β-amyloid in the aging brain. The Journal of Neuroscience, 25(4), 823-829. doi:10.1523/JNEUROSCI.4335-04.2005 Diz-Chaves, Y., Pernía, O., Carrero, P., & Garcia-Segura, L. M. (2012). 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