﻿WEBVTT

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How's this?

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That's perfect. Um, that is perfect, thank you. We will go ahead and get started, since it's already noon.

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So, welcome everyone to this Reskill Learning webinar series from Sales to Solutions.

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Emerging tools for studying health and disease. This is the second session, 3D Models and Technologies to Illuminate Biological Effects of Contaminants.

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This webinar is sponsored by the National Institute of Environmental Health Sciences.

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Superfund Research Program. My name is Molly Velasco, and I am a support contractor with the NIEHS Superfund Research Program.

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We will get started in just a few moments, but while we wait for others to log on, I will cover a few housekeeping items.

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So, when you registered for today's webinar. You should have received a confirmation email with instructions to join us for the live event.

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We also send the same instructions. Um, in our reminder email yesterday.

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Those emails will both point you to the seminar homepage.

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I encourage you to check it out, as there are important pieces of information.

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including the session description, contact information for our presenters.

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We will cover a number of important reminders, such as how to share your feedback on this webinar.

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This presentation has been provided as part of a U.S. Environmental Protection Agency webinar.

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or guarantee the validity of the information provided. Links to non-EPA servers are provided solely as a pointer to information that might be useful to EPA staff and the public.

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With that, I will now turn it over. to our moderator, Dr. Thad Shook from NIEHS, for opening remarks.

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that whenever you're ready.

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Good afternoon, everyone. I'm Pad Shugg. I'm a program officer at NIEHS.

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So, it's my pleasure to introduce the first speaker.

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We'll start with Steven Ferguson, an investigator with the mechanistic toxicology branch of the Division of Translational Toxicology, or DTT.

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Leading multiple research initiatives. to model and predict human responses to chemical exposures.

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He will discuss liver and kidney spheroid cultures. used to model chemical toxicity and disease.

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So, Dr. Ferguson, I'll turn it over to you.

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Thank you, Thad, and let me share my screen…

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Okay, so you able to see my screen and hear me?

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Yes.

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Yes. Perfect. Well, thank you so much for, uh, inviting me today, all the organizers, uh, particularly.

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Uh, given that Bev and Englewood, who I am not, was not able to be here today, but I am excited to share some of the work that we've been doing as we are.

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both kindred spirits and our aspirations for organotyping. in vitro models that help us better understand chemical toxicity and safety.

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Today, I'm going to share many of the learnings that we've had over recent years.

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towards advancing translational toxicology research with these types of models, and I must acknowledge, as a federal employee that I have no financial relationships to disclose, and the statements and opinions and conclusions that I make are.

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are my own. So… In the early models of human liver.

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Uh, such as these, these Hep G2 cells that you're seeing on the right, uh, these immortalized cancer cells that are proliferating on a plastic dish.

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They… they hold little resemblance to the functional elegance and complexity of human liver tissue and.

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This is, you know, while these models have been useful, this is a particular challenge. These cells are proliferating, they're.

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adhered to rigid plastic and really incapable of many of the differentiated hallmarks that we might observe in the.

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in the organ. But we've learned a great deal in recent decades about how to model liver epithelium using patient-derived cells.

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To better resemble the architectures. So you see here in this small caption, this cobblestone-like network of cells.

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And you're seeing that when those primary cells are isolated with sufficient viability and fidelity.

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And they're able to be reassembled into. tissue-like architectures that begin to behave much like the tissues, and so this is.

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An exciting opportunity. to begin to evaluate chemical safety with microphysiological systems.

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However, a major challenge with. these patient-derived cells is once they're ripped out of their native architecture.

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Uh, they rapidly de-differentiate, and without intervention, these cells will essentially become.

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uh, you know, dead. They just lose all their viability. They do have some short-term applications in drug metabolism, but outside of that.

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Uh, it's a real challenge to do this work. However, pioneering work from one of my mentors and many others in the field.

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Uh, in this case, uh, highlight Ed Leclus and his colleagues, uh, revealed critical factors for reestablishing epithelial-like canalicular networks.

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with these patient-derived cells to allow them to begin to manifest hallmarks of hepatocellular function.

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The key to this is culturing the cells with sufficient density.

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to enable them to be more three-dimensional, to be able to enable them to be more, uh.

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cuboidal in their structures that resembles better the in vivo architecture.

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And in doing so, we see rescue and recovery, maintenance of a number of hallmarks, such as drug metabolism activity.

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and signal transduction pathways that regulate the expression of.

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Uh, drug metabolizing enzymes and a myriad of other.

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transporters and related toxicological. Pathways. And so, these fundamental principles appear to be operative for many other epithelial tissues as well, not just the liver.

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Uh, but we're… we're learning from this over recent decades, and how we can begin to use these principles.

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to develop more sophisticated microphysiological systems that. are able to achieve tissue-like functionality, and.

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The good news is many of these systems have actually matriculated from concept and research into regulatory context.

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Presently, creating these types of culture systems and integrating assay platforms that allow us to make.

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interpretations and predictions for drug metabolism and drug-drug interactions can enable us to then make regulatory decisions and put.

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labels on new drugs that basically indicate whether there's a likelihood.

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of a response, whether clinical trials are needed. And so, the challenge we have is that for chemical safety research, this is not the case as we are.

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trying to much more extensively cover the myriad of effects that could happen in an animal or in a human.

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And in… along that route, we collect more than 120 tissues in a guideline animal study with clake biofluids. Many, many things can happen.

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And what's even more challenging is that these culture models, while they've been effective, are really limited. The traditional culture systems are in static.

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culture conditions in these sort of semi-2D environments, they exhibit poor nutrient exchange and are tethered to rigid plastic.

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in a survival mode that has super physiological concentrations of insulin and many other factors.

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And so these are, in essence, dying disease models that have a limited utility, but for chemical safety research.

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are really challenging, and so that's led to. sort of an explosion of different tissue engineering systems that have envisioned a way to sort of maintain.

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patient-derived cells with higher fidelity for weeks and months of exposure that include three-dimensional platforms.

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Microfluidic and barrier models, as well as multi-tissue axes, where we begin to.

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combine the liver and, say, the thyroid or other models.

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That, uh, that these tissues sort of work together in vivo in an axis of pathophysiology in response to chemical exposures. And so, how can we begin to.

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Look at this landscape of things alongside, uh… useful, uh, enzyme and biomarker assays to then begin.

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begin to make decisions about chemical safety research. And these systems really do have a lot of potential, but.

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Uh, what's challenging right now is that we're not able to fully establish the context of use for all these different systems. There's a wide range of them.

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And then we ultimately have to do the heavy lifting to qualify these systems, to calibrate how to use data from these systems with human therapeutics.

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to understand xenobiotic exposure responses with environmental chemicals, drugs, botanicals.

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and other… other things. So, to address these needs, we've been advancing research and development efforts in multiple avenues, and one of the key partnerships that I'd like to highlight today.

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has been our work with the TIX VAL Consortium, led by Von Rusen at Texas A&M.

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Uh, to explore the landscape of these different systems in collaboration with industry and government researchers.

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Uh, led by laboratory technical experts like Courtney Sokolish in his lab. The TEXVAL team has comparatively evaluated a range of microphysiological systems.

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And provided methods to partner labs like ours that help us to extend.

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Uh, this kind of technology that's coming out of academic research.

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into, uh… additional research applications, and so we're really excited about continuing this partnership as we evaluate a number of device systems and.

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Look at clinical biomarker assays. In our laboratory here at NIHS, we've been working to extend emerging science and technology to understand and predict human responses to drug.

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natural product and environmental chemical exposures for many years, and our laboratory.

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looks to develop these microphysiological systems. alongside biomarker assays and high-dimensional assays that give us mechanistic insights.

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And then, ultimately, using computational models, interpret those assays into decision context. And we've been doing that work for quite a while.

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Uh, and really, our primary aims are to develop and qualify these physiologically relevant.

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microphysiological systems and assays into NAMS that are actually relevant.

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Uh, and useful. And to lead into innovative toxicological investigations of environmental substances, and I'll speak about some of our work today on PFAS and aqueous film-forming foams.

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And then, to address critical gaps in NAMM-based toxicology research.

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Our pioneering work in introducing free-floating spheroid cultures in human hepatocytes for chemical safety research.

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has revealed these little powerhouse liver microtissues can be.

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robust, uh, little engines that are able to emulate.

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hallmarks of hepatocellular function, and what's really great about these is they support not just days of exposure that we can see in our 2D cultures.

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but actually months of high-fidelity functionality. They're able to then, uh, as a result of that.

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Help us to predict the potency ranges for drug-induced liver injury and their highly efficient and cost.

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cost efficient, and as they use so many fewer cells compared to a standard two-dimensional culture model. And this is the type of model that Bevin and I have been working on for a number of years.

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And we're really excited to see how these can work. And in particular, I would just highlight the fact that they begin to polarize and form.

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Uh, liver-like architecture, uh, just spontaneously, that's much more elaborate than what we see in two-dimensional cultures.

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Now, one of the sort of key… hallmarks of hepatocellular function that's really distinguished the less evolved or differentiated systems like iPS-derived hepatocytes at HEPG2 cells.

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from the liver tissue and suspensions of hepatocytes that we've seen is their drug metabolism proficiency.

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And so, in this, this sort of, uh, this is your life photo, you see an example on the left where we're looking at the median.

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Drug metabolism activity for CYP1A2, 2B6, and 3A4 across hundreds of donor preparations of human hepatocytes.

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And so, in comparing that median to where we were in TOX 21, uh, in using immortalized cells.

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You can see we had just minimal metabolic activity for these major clinical enzymes that are important for drug clearance in humans.

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And then 2D models of human hepatocytes, you can see how they're about only 10% of what we see.

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Uh, in terms of their initial starting point. So even then, we see that they're de-differentiating to some extent.

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But what we were excited to discover is that when we took.

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Uh, the surrogate for primary human hepatocytes that we've been using, these HIPAA-RG cells, we found that.

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When you cultured them in increasingly sophisticated culture conditions.

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that we saw a dramatic increase in the enzymatic activities that began to rival what we see in the median suspension human hepatocytes. And so.

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This suggests not only that they're able to. to be responsive to… to… to the culture conditions, but they're also indicating that there's something really special going on in these free-floating microtissues, and I'll talk a little bit more about that later.

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Um, but what we're excited about is not only are these metabolically proficient, they're also able to retain liver-like signal transduction pathways. They're not just emulating zone 3 of the liver.

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But they're further inducible, analogous to liver tissue. to mimic these major hepatic receptor signaling pathways, many of which are involved in cancer.

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And to polarize, as I mentioned earlier, to form these biliary excretion networks that enable them to.

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to not be cholestatic, but to actually be a viable model that's actively, uh.

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effluxing bile acids into these bile pockets, and then ultimately out into the media.

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But with their small size, that dilution is quite good, and with the Brownian motion that can happen in moving around, we think that they're really exquisite in their ability to exchange nutrients and waste products and achieve this level of metabolic proficiency.

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And we found that when we looked at drug analogs, like trofloxacin versus levofloxacin, that had varied.

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clinical outcomes for liver injury, we're able to readily distinguish the hepatotoxic molecules from the non-hepatotoxic molecules.

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troglitazone and rosiglitazone was another example, and we've had many of these while we look at molecules like aspirin and gemfibrozil that have.

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Minimal reports of liver injury, and these models seem to be able to emulate that type of effect, and we've dug more deeply into these mechanisms and pathways.

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Uh, and we've also applied them in some ways to external things. So botanicals are particularly an area where we have intentional human exposures.

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And Adam Pearson in the lab was able to take these microtissue type models and apply them under our botanical safety consortium research.

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Uh, using these 384 wall plates. And a combination of cell painting and diagnostic-type assays for liver enzyme leakage and albumin production.

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And CYP3A4 inhibition. As well as transcriptomics have enabled us to have, uh, create data for a number of manuscripts in this space.

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And really demonstrated to us the power of these little microtissues.

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to inform a variety of applications, and I'll talk a bit more about some of those in the next few slides, but.

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One of the things I wanted to highlight to folks is that.

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when we look at, um, the longevity of 2D.

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primary rat hepatocytes. It's typically 3 to 5 days, and then the cells really start.

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Excuse me, starting to struggle and die. But those same cells in these 3D microtissues have months of longevity.

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And not only longevity, but functional longevity, and able to sort of.

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rescue metabolic proficiency, uh, respond to those CAR-type activators and other signaling pathways.

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and stain histologically in collaboration with Dr. Darlene Dixon, to reflect the same types of architecture that we see in liver tissue, in this case, glycogen staining and.

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CK19 staining for, um. cholangiocyte-like cells.

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And what this enables… is now an ability to bridge the gap between our animal studies and our human studies using this parallelogram-type approach of microtissues that we can compare between rat and human, and we know these systems do emulate.

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Um… interspecies comparisons, and the molecular potencies across species can oftentimes be very predictive.

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And so we're excited to see how this type of enabling technology.

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can expand to complement. our animal studies, and really, due to their small size, even give us an opportunity to reduce the number of animals that we're using in toxicology research while we're.

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building confidence in their context of use. So, we've also been integrating omics assays, and a few years back, we published this Power of Resolution Manuscript.

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that describes our efforts to develop high-throughput transcriptomics with these types of models.

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Uh, and we were able to successfully show that this platform defined a threshold.

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transcriptomically defined threshold. that enables you to define the relative potency.

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across a range of compounds based on where they cross this threshold.

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And using these types of data, we can now distinguish drug-induced liver injury compounds like trofofloxacin and levofloxacin.

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both qualitatively and in terms of their relative potencies. And so that begins to create an opportunity for predictive toxicology and chemical safety.

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that better defines margins of exposure, and the potency ordering of those firing sequences that occurs between.

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biological effects that might be off-target or, you know, reversible adaptive responses relative to those that are stressful and cytotoxic.

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is a key opportunity within these types of data to just sort of.

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resolve the relative potencies of biological responses, and then relating those with.

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biomarkers of clinical pathology and cellular imaging begins to build confidence, and one example that I highlight here is with aflatoxin.

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where we were actually able to observe scarring that occurred in these 2D cultures of Hepner RG.

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And we were able to observe clearly that at those same concentration ranges, we were getting molecular pathway responses related to injury and repair and DNA damage.

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And so this type of response with aflatoxin B1 just highlights the potential for these types of systems.

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to more comprehensively inform chemical safety research. And we're excited to see where these can go. And we've actually applied them recently in an ES&T publication.

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Uh, where we've been looking deeply in support of the Department of Defense and their needs to identify safer aqueous film-forming foams for military use.

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And in our coordination with them, published this manuscript.

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that basically is highlighting an evaluation of 30 test substances.

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that included 5 aqueous film-forming foams, and a number… a large number of PFAS perfluorinated alkyl substances.

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As well as human drugs that help to anchor the data set.

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And in this work, we were able to use a combination of this transcriptomic thresholding approach.

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Uh, to predict the potencies for liver injury. We were also able to use multiple data streams to build a weight of evidence for that in these systems.

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Uh, we were able to, as with the drugs, we were able to identify mechanistic pathway potencies.

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And then, to define biological response similarities, such as what you see here by comparing PFAS, which is a very extensively studied PFAS and is known to be toxic.

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with structurally similar but shorter chain PFH excess. And this poorly understood and data-poor molecule, 6-2 fluoroteomer sulfonate.

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And what we see is that they share a great deal of biological response similarity in these human hepatocyte microtissue models.

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And so the idea is to continue to. to help support our regulatory needs for read-across, and this type of data help us to decide whether these alternative or more modern molecules are toxic, and what's the relative potency.

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Uh, for those. We also have expanded that biological response similarity analysis to sort of more fully.

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capture which chemicals are similar to one another, but more importantly, to anchor their.

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Their aggregate biological effects at the very low concentrations.

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Uh, with… with model compounds like YF14643, which is a known activator of the peroxilone proliferator activator receptor alpha.

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Or, uh, omeprazole and phenobarbital, which can activate the pregnant X receptor and.

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the constituent of Androsane receptor, as well as a cluster here that was just containing cyclosporin A and a bunch of aqueous film-forming foams that might be more related to lipid disruption, as we know.

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cyclosporin A can cause fatty liver. And so, taking all of these sort of similarity relationships in mind, we can begin to also think about not only supporting our.

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our EPA colleagues and read across, but we also can begin to predict.

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Apical outcomes, and so in this case, we took the relative potencies for car.

00:21:50.000 --> 00:21:59.000
PPAR activation and liver injury. that we, uh, that are well-established modes of hepatomegaly, and then to use that.

00:21:59.000 --> 00:22:05.000
To predict whether we are, uh, what are the concentrations in vivo in the animal.

00:22:05.000 --> 00:22:09.000
And those are shown in the blue, or the purple triangles here.

00:22:09.000 --> 00:22:20.000
The concentrations at which we see. Um, in vivo effects to enlarge the liver, and what we're seeing is that when we look at these pathway potencies in human hepatocytes.

00:22:20.000 --> 00:22:26.000
relative to the in vivo liver weight lobe, we're getting a reasonable overlap, and so we're able to predict.

00:22:26.000 --> 00:22:40.000
The animal OL using internal doses. And we've taken all these types of data and begun to extend them both in terms of our in vivo investigation of PFAS bioaccumulation from aqueous film-forming foam exposures.

00:22:40.000 --> 00:22:45.000
Our in vivo biology from AFFF exposures and our in vitro mechanistic data.

00:22:45.000 --> 00:22:54.000
Uh, to begin to… to… to enable development of prioritization frameworks that can identify safer products.

00:22:54.000 --> 00:23:01.000
And ultimately, uh, help to improve our environment with safer options.

00:23:01.000 --> 00:23:10.000
So, we've also identified that PFAS accumulation is one of the fundamental concerns with, um.

00:23:10.000 --> 00:23:15.000
with PFAS, and we've been able to use tissue chip platforms, such as the Emulate platform.

00:23:15.000 --> 00:23:25.000
To demonstrate we can distinguish long and short half-life PFAS from one another, uh, based on their renal reuptake. So in this case, we established a kidney, uh.

00:23:25.000 --> 00:23:33.000
tissue chip system, and we're able to show PFAS extensively accumulated in epithelial cells from apical exposures compared to.

00:23:33.000 --> 00:23:43.000
PFBS. And we've done similar work with the liver and liver microtissues to demonstrate distinctions between the long and the short chain.

00:23:43.000 --> 00:23:51.000
PFAS, and we're also interested in addressing the more than 15,000 PFAS that have been identified in Commerce.

00:23:51.000 --> 00:24:01.000
Uh, by the US EPA in recent, recent, uh, recent publications, and to use computational models, uh, including the bioconcentration factor, to help stratify.

00:24:01.000 --> 00:24:07.000
PFAS, even if they don't cross historical thresholds, and using combinations of.

00:24:07.000 --> 00:24:16.000
of bioconcentration and hepatic clearance to be able to tier these molecules, these more than 15,000 molecules, into testable.

00:24:16.000 --> 00:24:29.000
units that help us fill the data gaps. I want to switch back to the three-dimensional microtissue models now, and just show you a couple examples where these micro-tissue models in 3D.

00:24:29.000 --> 00:24:42.000
convey superior, uh, ability to distinguish hepatotoxicant. responses with valproic acid and cyclophosphamide. And so here, uh, we're looking at two compounds that require metabolic activation.

00:24:42.000 --> 00:24:57.000
And what we see is robust responses in 3D compared to very small responses in 2D cultures. And so, these are two of the sort of less common examples, but clear examples, where metabolic activation.

00:24:57.000 --> 00:25:08.000
Uh, maybe a toxicity-determining step. Um, with benzoylpha-pyrin, we actually saw the opposite effect. With our proliferating HIPAA-RG, we saw they were more sensitive.

00:25:08.000 --> 00:25:12.000
than the 3D microtissues, and this may be related to.

00:25:12.000 --> 00:25:20.000
the fact that the benzoylfa pyroine is causing DNA damage, and the rate determining step for toxicity is different, and so.

00:25:20.000 --> 00:25:31.000
One of these may be more predictive than the other, and we're continuing to investigate this, but we… it's not always the case that three-dimensional cultures are more sensitive, and so we're digging into this more deeply.

00:25:31.000 --> 00:25:37.000
And we've done this type of analysis for many, many drugs, and one of the sort of interesting.

00:25:37.000 --> 00:25:42.000
trends we've seen. When we look at transcriptomic pathway enrichment.

00:25:42.000 --> 00:25:47.000
is that 3D hepatocyte cultures tend to be much more extensively enriched.

00:25:47.000 --> 00:25:54.000
for anticipated or known targets of these compounds. So you're looking at a range of compounds that have.

00:25:54.000 --> 00:26:00.000
known targets, fenofibric acid for PPAR signaling. phenobarbital for car signaling.

00:26:00.000 --> 00:26:05.000
rosiglitazone for PPAR signaling, and what we see across the board.

00:26:05.000 --> 00:26:16.000
Uh, is a better enrichment in 3D compared to 2D culture models, and so… In aggregate, this is telling us something in addition to the fact that many of these models are more predictive.

00:26:16.000 --> 00:26:22.000
Uh, across the board, and we're excited to see how this type of knowledge can then really.

00:26:22.000 --> 00:26:38.000
increase our ability to do predictive toxicology. Um, just want to highlight near the end here, just a couple of quick, uh, points. So, we've been working, uh, not only in liver, which is the vast majority of our work, but Adam Pearson also established in our lab.

00:26:38.000 --> 00:26:50.000
methods for looking at proximal tubule. Uh, we particularly know that the kidney is one of the target tissues of highest concern, and the proximal tubule being the most vulnerable.

00:26:50.000 --> 00:26:57.000
And he discovered that these small microtissues of renal proximal tubule cells actually remember.

00:26:57.000 --> 00:27:01.000
how large the proximal tubule was in vivo, and they just auto-assemble.

00:27:01.000 --> 00:27:11.000
into these small tubuloids is what we're calling them. And in comparing the 2D cultures with domes, so these would be considered a differentiated 2D culture.

00:27:11.000 --> 00:27:22.000
that's forming a fluid pocket under the epithelium. Uh, we're seeing sensitized response to compounds like cisplatin, and we've done a number of compounds.

00:27:22.000 --> 00:27:28.000
about 37 compounds we've screened with this platform, and those publications are in.

00:27:28.000 --> 00:27:37.000
in preparation. And finally, I just want to leave you with a couple of thoughts. When I joined the NIHS, one of the big things that we were concerned about is.

00:27:37.000 --> 00:27:46.000
Uh, you know, in an animal model, anything could happen. So we're trying to understand what it is that we can predict with NPS and NAM-based systems, and.

00:27:46.000 --> 00:27:54.000
To address this question, we first need to understand, well, what do we normally look for? And so, I turn to the NTP's histopathology glossary.

00:27:54.000 --> 00:28:00.000
Um, where there are a thousand lines of things that a pathologist could find in an animal.

00:28:00.000 --> 00:28:07.000
And I basically started to map. those morphologies and those locations, and trying to then say, well.

00:28:07.000 --> 00:28:14.000
in a liver microphysiological system, what could we potentially see with the existing or emerging models?

00:28:14.000 --> 00:28:20.000
And then work to develop a Rosetta Stone that translates liver MPS data into.

00:28:20.000 --> 00:28:33.000
recognizable pathology findings that we can then meet the regulators and other decision makers in a more recognizable place, and then ultimately calibrating those with drugs so that we can quantitatively use them.

00:28:33.000 --> 00:28:39.000
And just to show you a high-level summary of what I was able to determine, but essentially.

00:28:39.000 --> 00:28:44.000
even though we're only looking at one tissue out of the 120 that you might collect.

00:28:44.000 --> 00:28:50.000
Uh, and we're not really able to identify all the locators across all of pathology.

00:28:50.000 --> 00:29:01.000
We are starting to make an impact in the number of morphologies and modifiers that we could observe there, and I'm going to be going more into this and partnering with folks in pathology to.

00:29:01.000 --> 00:29:08.000
to sort of roll these out and vet them as we go further, but I think the initial point is to say we're trying to understand.

00:29:08.000 --> 00:29:16.000
what it is we want to predict, and then to tune microphysiological systems towards these endpoints that can then be used in decision making.

00:29:16.000 --> 00:29:27.000
And finally, I'm going to leave you with feature directions. We're already working to, uh, you know, manifest toxicological phenotypes, as I mentioned, and this pathology sort of mindset.

00:29:27.000 --> 00:29:36.000
Uh, we also want to begin to do a much better job in addressing factors of inter-individual susceptibility to chemical exposures.

00:29:36.000 --> 00:29:41.000
Uh, we have, oftentimes, adult models, because that's where clinical trials are run, and.

00:29:41.000 --> 00:29:47.000
But we don't have models of fetal, although iPS-derived cells.

00:29:47.000 --> 00:29:52.000
could be used in that way. Uh, geriatric childhood neonatal, we don't have those.

00:29:52.000 --> 00:29:59.000
Uh, it's sad to say we don't have. sexually dimorphic culture conditions for hepatocytes.

00:29:59.000 --> 00:30:07.000
We put them in a monosex medium, um, that… and we may use donors from a male and female, but we need to do a much better job of this.

00:30:07.000 --> 00:30:26.000
Um, genetic predisposition and disease haplotypes, and then. Probably most importantly, from a susceptibility standpoint, is modeling pre-existing disease, like steatosis. We're starting to do that now with high-fat media, and then looking to see how these might differentially sensitize.

00:30:26.000 --> 00:30:36.000
Uh, to chemical toxicity. And then finally, just expanding tissue coverage and axes of pathophysiology, as I mentioned earlier, the liver, thyroid, axis.

00:30:36.000 --> 00:30:42.000
And the concerns with PFAS. So, with that, I'll be happy to take any questions and just really.

00:30:42.000 --> 00:30:51.000
It's an honor to work at the NIHS, and it was such an amazing group of talented scientists, and thank you for your time.

00:30:51.000 --> 00:30:58.000
Thank you, Steve. Um, so, listeners, you can enter questions through the, um, question-answer pod.

00:30:58.000 --> 00:31:13.000
And looks like we have a few already on deck here, so… How do you deal with floating HEPA RG cells that do not readily aggregate into spheroids?

00:31:13.000 --> 00:31:32.000
Yeah. So if the HEPARG cells are not aggregating into spheroids, there's probably something, uh, not… ideal in the cultural conditions. They will self-aggregate if the cell numbers and the cell configurations are correct, and we often find a more conical.

00:31:32.000 --> 00:31:40.000
uh, shape will make that happen faster, but it typically takes between 3 and 7 days for those cells to coalesce into a microtissue.

00:31:40.000 --> 00:31:51.000
Now, once they're formed into that microtissue, we do use special plates, and there are a few different types. Some plates are more or less sensitive to the floating.

00:31:51.000 --> 00:32:03.000
But we use standard liquid handler, in our case, the Viaflo, that we stamp a 384-wheel plate, we remove half the media, and in some cases, we remove 80% or 90% of the media.

00:32:03.000 --> 00:32:14.000
And then process the cells that way, but it's, it's pretty straightforward. The primary hepatocytes tend to be more dense than the HEPARGs after about 10 days in culture.

00:32:14.000 --> 00:32:28.000
Um, so that's… that's one distinction that we've observed, but… but that's how we handle floating HepRGs, is that they… they settle to the bottom, and with liquid handling, where you're only exchanging about half the medium every other day or every day.

00:32:28.000 --> 00:32:31.000
It's no problem.

00:32:31.000 --> 00:32:38.000
Okay, uh, next question. Can you comment on how your assays, such as HEPARG, stack up?

00:32:38.000 --> 00:32:43.000
Oh, it's all good. Got it. Fix this here, wait.

00:32:43.000 --> 00:32:45.000
Just one second… Yes, I guess most models, do you see the same responses?

00:32:45.000 --> 00:32:50.000
Against mouse models, I think that's it, yeah.

00:32:50.000 --> 00:32:58.000
Yeah, we haven't made mouse, uh, spheroids yet. Uh, we've made rat, we feel very comfortable that we're seeing, um.

00:32:58.000 --> 00:33:02.000
things that make sense there. We know that 2D models of mouse.

00:33:02.000 --> 00:33:08.000
are good, but very short-term. They're even shorter-lived than the rat.

00:33:08.000 --> 00:33:15.000
Um, and so… but there have been reports of mouse spheroids being formed, and they should be a good model.

00:33:15.000 --> 00:33:31.000
And again, you would use far fewer mice, because they don't eat well, would require a very small amount of cells, and so, um… I'm very encouraged by what I've seen so far with the rat, and… but we haven't done the mousework yet.

00:33:31.000 --> 00:33:40.000
Okay, thank you. So, are you comparing biological pathway readouts using MPS, etc, with responses seen in human population studies?

00:33:40.000 --> 00:33:43.000
If so, how do these compare?

00:33:43.000 --> 00:33:50.000
Yeah, we haven't… we haven't, in our lab, gotten to that point. I think we… we would be looking to partner with researchers who.

00:33:50.000 --> 00:34:01.000
have existing, you know, epidemiological observations and hypotheses, and what we're thinking about is more developing those states of susceptibility.

00:34:01.000 --> 00:34:05.000
And we don't know what our end's gonna be yet for any given state.

00:34:05.000 --> 00:34:19.000
But the idea is to capture those states, and then we'll do power calculations to understand how many we would need to see what effect. And for acute effects, the numbers probably won't be that large, but when we start to get to something that's slower developing.

00:34:19.000 --> 00:34:24.000
And it takes much longer exposure. The end's gonna likely increase, and so I think.

00:34:24.000 --> 00:34:29.000
That's where the scientific community has to decide what's the value of.

00:34:29.000 --> 00:34:45.000
you know, digging deeper compared to the decisions you could make shorter term. But, um, you know, that… we're a long ways from being able to do that type of work, but the technology at scale is there to do it.

00:34:45.000 --> 00:34:51.000
So the next question, are we missing the inflammatory contributors to toxicology?

00:34:51.000 --> 00:34:53.000
our toxicity in these models, and any comments?

00:34:53.000 --> 00:35:07.000
That's a… that's a great comment, and we're… we are and we're not, so… Some of the models that I showed you have resident macrophages, the Kupfer cells that are already in these microtissues, and.

00:35:07.000 --> 00:35:16.000
When they're in a happy 3D microtissue, they become quiescent if they're not already, typically they're already isolated to be quiescent.

00:35:16.000 --> 00:35:27.000
Um, and then they will become activated when toxicity occurs. What we don't have is circulating macrophages in your typical microtissue model.

00:35:27.000 --> 00:35:51.000
And so, being able to see infiltration and a lot of things you're going to see in pathology is something that could be done, might be more amenable to some of the tissue chip systems where there's been some progress with that, but it could also work with microtissues with the right tuning. We just haven't gotten far enough to do that, but there is an inflammatory component there, but it's not… the amplifier is probably not there to really.

00:35:51.000 --> 00:35:57.000
uh, you know, manifested, you know, an organ-level toxicity.

00:35:57.000 --> 00:36:03.000
Okay, next question. What might be correlated more by microtissia 3D systems, the toxokinetico.

00:36:03.000 --> 00:36:07.000
Technetic or toxico… dynamic aspects.

00:36:07.000 --> 00:36:15.000
Well, if we've done it properly, it should be both, but um… That's a great point. These microtissues.

00:36:15.000 --> 00:36:24.000
are very small, and so they don't… They don't reflect the allometric scaling of blood to liver.

00:36:24.000 --> 00:36:28.000
And so we have to tune and calibrate these systems.

00:36:28.000 --> 00:36:37.000
for the decision context that they're useful for, but what I can say as a general principle is if we've modeled the toxicokinetics.

00:36:37.000 --> 00:36:46.000
Real… in a relevant way. the Tosico dynamics and the translation of an individual effect, whether it's benign or toxic.

00:36:46.000 --> 00:36:55.000
should be more accurate. And what we're seeing in these microtissue models and other MPS systems, that they have a better capacity to.

00:36:55.000 --> 00:37:05.000
partition their own internal exposure, uh, better than we would think, but still, um, they're going to be limitations unless we have.

00:37:05.000 --> 00:37:13.000
a full accounting for that, and that's why I'm… really interested in pooled spheroid models, where we can have a much bigger liver than we do a thyroid, or.

00:37:13.000 --> 00:37:18.000
other tissue so that we can try to scale those axes to have metabolomic.

00:37:18.000 --> 00:37:29.000
endocrine… paracrine signaling that's more equivalent to what we would see in VO, and how those tissues would adapt and interact with one another.

00:37:29.000 --> 00:37:37.000
Okay, um, thanks a lot for your presentation, Steven, it was… Terrific, and also perfect timing.

00:37:37.000 --> 00:37:45.000
So, let's move on to our, um, second presentation today. Next, we have Susan Tilton.

00:37:45.000 --> 00:37:50.000
Associate Professor in the Department of Environmental and Molecular Toxicology.

00:37:50.000 --> 00:37:55.000
At Oregon State University and a project leader at Oregon State University.

00:37:55.000 --> 00:38:05.000
Superfund Research Center. Her lab uses molecular and computational tools to predict toxic… toxicity of chemical contaminants in the environment.

00:38:05.000 --> 00:38:11.000
Dr. Tilmutter introduced a 3D human lung respiratory model of asthma.

00:38:11.000 --> 00:38:24.000
So, Dr. Tilton? Please feel free to begin when you're ready.

00:38:24.000 --> 00:38:29.000
All right, thank you.

00:38:29.000 --> 00:38:34.000
So let me see, um…

00:38:34.000 --> 00:38:38.000
just make sure that you can hear me okay, and you can see my slides.

00:38:38.000 --> 00:38:39.000
Yes, we can.

00:38:39.000 --> 00:38:46.000
Okay. Um, well, thank you for that introduction, um, and thank you for the invitation to speak today.

00:38:46.000 --> 00:38:52.000
Um, as that said, I'm an associate professor and principal, um.

00:38:52.000 --> 00:39:00.000
Project principal investigator, uh, for the Oregon State University and Pacific Northwest National Laboratory Superfund Research Center.

00:39:00.000 --> 00:39:04.000
Uh, so today, I plan to share with you, um.

00:39:04.000 --> 00:39:10.000
Some of our work using primary human bronchial epithelial cells cultured at the air-liquid interface.

00:39:10.000 --> 00:39:15.000
As a 3D model to investigate health effects of polycyclic aromatic hydrocarbons.

00:39:15.000 --> 00:39:23.000
associated with, um, both contaminated sites and wildfire smoke.

00:39:23.000 --> 00:39:32.000
So I'd like to begin, um, just by briefly highlighting our center and, um, our integrated projects and cores.

00:39:32.000 --> 00:39:39.000
So our center is titled, uh, the Center for Science, Technology, and Emerging Health Risk of PAHs.

00:39:39.000 --> 00:39:45.000
It's, uh, driven by a mission to identify pHs in the environment, characterize their toxicity.

00:39:45.000 --> 00:39:51.000
determine environmental concentrations below which they pose minimal risk to human health.

00:39:51.000 --> 00:39:58.000
And also to develop safe and sustainable approaches for remediating pH-contaminated sites. So.

00:39:58.000 --> 00:40:05.000
Um, overall, our goals are to understand the composition of these complex mixtures containing PAHs.

00:40:05.000 --> 00:40:15.000
how they can change in the environment, and the implications for both these pHs and mixtures for human health.

00:40:15.000 --> 00:40:23.000
Uh, research program relies heavily on the use of integrated, um, new approach methodologies, or NAMs.

00:40:23.000 --> 00:40:30.000
So this includes, um, cell-based systems, non-mammalian whole animal models, like superfish.

00:40:30.000 --> 00:40:39.000
And in silico approaches that are used, um. Throughout the program, and today I'll talk about some work in collaboration, in particular with.

00:40:39.000 --> 00:40:43.000
Jordan Smith in the predictive dosimetry and Metabolism core.

00:40:43.000 --> 00:40:49.000
Um, also coupled to passive sampling techniques to quantify environmental fate.

00:40:49.000 --> 00:40:58.000
and human exposure to chemicals. So together, these tools allow us to efficiently link environmental measurements with biologically relevant.

00:40:58.000 --> 00:41:04.000
human outcomes. Some of the key goals, uh, for my project in particular.

00:41:04.000 --> 00:41:14.000
Um, include using 3D respiratory models to establish quantitative relationships between chemical exposure and toxicity.

00:41:14.000 --> 00:41:21.000
advancing these systems… Um… to predict pH toxicity in susceptible populations.

00:41:21.000 --> 00:41:32.000
And then understanding mechanisms, uh, driving lung toxicity from novel substituted pHs, and those in complex mixtures. So this is particularly relevant.

00:41:32.000 --> 00:41:41.000
For, um, multi-source exposures near Superfund sites, which in the Pacific Northwest often include, um, concurrent exposures.

00:41:41.000 --> 00:41:49.000
Uh, to wildfire smoke, for example, among others. So I'll focus on some of these goals today.

00:41:49.000 --> 00:42:04.000
In addition, within our program, an essential component is just the engagement with state and federal agencies, um, industry partners, and local communities, so through these collaborations, uh, we communicate our science to support informed decision making.

00:42:04.000 --> 00:42:14.000
related to the assessment, management, and mediation, remediation of contaminated sites throughout our region.

00:42:14.000 --> 00:42:19.000
So I've mentioned that our program focuses on polycyclic aromatic hydrocarbons. Um, these are.

00:42:19.000 --> 00:42:26.000
Uh, ubiquitous contaminants in the environment that can occur from both naturally occurring and anthropogenic sources.

00:42:26.000 --> 00:42:32.000
pHs account for 3 of the top 10 chemicals of concern at priority pollutant sites.

00:42:32.000 --> 00:42:48.000
And are associated with multiple adverse health effects. Our Superfund program in particular, um… Over a number of years has identified both parent PHs and transformation products that are formed in the environment.

00:42:48.000 --> 00:42:59.000
Um, across, uh, multiple phases in soil, water, and air, um, associated with Superfund sites and other hazardous waste sites.

00:42:59.000 --> 00:43:03.000
In addition, I wanted to highlight, um, through some of the work.

00:43:03.000 --> 00:43:09.000
Uh, and Kim Anderson's, uh, project, um, so she's a project lead in our program.

00:43:09.000 --> 00:43:14.000
Uh, working towards identifying, um, that alkylated pHs in particular.

00:43:14.000 --> 00:43:21.000
rank among the most abundant pHs measured in environmental samples, um, from multiple sources. So this includes.

00:43:21.000 --> 00:43:27.000
Petrochemicals associated with Superfund sites, um, and thermal decomposition of organic matter.

00:43:27.000 --> 00:43:35.000
So, for example, in this case, we're passive samplers were deployed, um, in air and water at a browns-filled creosote site.

00:43:35.000 --> 00:43:52.000
Um, at all locations, um, and sampling dates. Uh, we can see that alkylated pHs that are summed here by the blue dots were more abundant, um, than the unsubstituted or parent pHs that are quantified by the orange dots.

00:43:52.000 --> 00:43:56.000
Um, so this is in both air and surface water.

00:43:56.000 --> 00:44:02.000
Um, and again, across all sites, um, and time points.

00:44:02.000 --> 00:44:09.000
Her group is also observed in passive sampling with wristbands, so these are used to measure personal exposure to PAHs.

00:44:09.000 --> 00:44:19.000
Uh, that seasonally, many of the more highly abundant pHs that are measured are 2- to 3-ring alkylated PAHs.

00:44:19.000 --> 00:44:26.000
Um, so some of the primary sources during summer are associated with wildfire smoke exposure.

00:44:26.000 --> 00:44:33.000
Or in the winter with, um, indoor sources, like, uh, indoor heating or cooking.

00:44:33.000 --> 00:44:44.000
So while priority PAHs. And those shown here, which include these 16 unsubstituted parent PAHs, are the ones that we continue to know the most about.

00:44:44.000 --> 00:44:49.000
Um, in terms of their toxicity. Their potential for human exposure.

00:44:49.000 --> 00:45:00.000
And frequency of occurrence at hazardous waste sites. Um, there are more than 1,500 chemicals total in the broader class of polycyclic aromatic compounds.

00:45:00.000 --> 00:45:07.000
That include pHs which with. diverse structural features, um, and substitutions.

00:45:07.000 --> 00:45:23.000
that we currently have very little data on in terms of sources, exposure, toxicity, and mechanisms. So… Overall, our program focuses on these novel pHs, and particularly these highly abundant alkylated PAHs, which are also found.

00:45:23.000 --> 00:45:34.000
As part of environmentally relevant mixtures. We have tested a number of these 3-5 ring alkylated, um.

00:45:34.000 --> 00:45:40.000
pH families for toxicity and primary human bronchioepithelial cells.

00:45:40.000 --> 00:45:49.000
And found that many of the alkylated pHs. Cause toxicity at lower concentrations than their unsubstituted parents.

00:45:49.000 --> 00:46:01.000
Um, or unsubstituted forms across multiple endpoints, uh, so including cytotoxicity, oxidative stress, mitochondrial membrane potential, um, and also including DNA damage.

00:46:01.000 --> 00:46:09.000
So, in this table, the asterisks, um, indicate that the alkylated pH, um, listed.

00:46:09.000 --> 00:46:17.000
cause a statistically significant response at a concentration lower than its corresponding parent. So all of the parents are highlighted in boxes, and they're.

00:46:17.000 --> 00:46:34.000
Responding alkylated forms are listed below. So while we're still in the process of… of analyzing this data, we can preliminarily say that we are observing that alkylated pHs may cause toxicity through unique mechanisms compared to their parent.

00:46:34.000 --> 00:46:41.000
Potentially also causing genotoxicity, um, uniquely compared to parent forms.

00:46:41.000 --> 00:46:49.000
And collectively, this data really suggests that current risk assessments may underestimate pH risk from inhalation exposure.

00:46:49.000 --> 00:46:58.000
due to lack of data and lack of our knowledge about contribution to toxicity from these alkylated forms.

00:46:58.000 --> 00:47:04.000
So, in order to study toxicity from inhaled pHs, our lab primarily works with.

00:47:04.000 --> 00:47:15.000
3D airway organotypic culture model. So, this is a cell system in which primary human cells are differentiated at the air-liquid interface, or ALI.

00:47:15.000 --> 00:47:22.000
Um, primary human bronchial epithelial cells are collected from donors and then cultured on a transmembrane insert.

00:47:22.000 --> 00:47:34.000
And, um, in this case, under conditions in which they're allowed to differentiate for approximately 25 days, uh, to induce a three-dimensional structure with these multiple cell types.

00:47:34.000 --> 00:47:38.000
Um, that mimic the lining of the bronchial epithelium.

00:47:38.000 --> 00:47:44.000
So in our model, the cells differentiate into the pseudostratified structure, um, with ciliated cells.

00:47:44.000 --> 00:47:51.000
Um, mucus producing goblet cells, producing stem-like basal cells, among others, um, to.

00:47:51.000 --> 00:47:58.000
Allow us to more accurately reflect. Um, exposure at tissue interfaces and better recapitulate.

00:47:58.000 --> 00:48:22.000
In vivo response. Towards the end of my talk today, I will spend some time highlighting how we are continuing to work, develop, and modify our ALI models to study disease phenotypes, um, also generate co-culture models to better reflect in vivo systems.

00:48:22.000 --> 00:48:32.000
Overall, and Steven referenced this very well in his talk, too, these types of advanced cell culture models and organotypic models.

00:48:32.000 --> 00:48:37.000
You know, which can range from these differentiated cell models, um, all the way to tissue models.

00:48:37.000 --> 00:48:42.000
are really an important part of this translational pipeline in toxicology.

00:48:42.000 --> 00:48:50.000
Helping us translate from Encylico and simple in vitro testing to what we know about adverse outcomes in humans.

00:48:50.000 --> 00:48:56.000
And while they can potentially, um… serve as a replacement for animal models.

00:48:56.000 --> 00:49:02.000
Um, and also serve to supplement our knowledge. Uh, from animals and human relevant systems.

00:49:02.000 --> 00:49:16.000
These complex models also allowed for translation to humans and improved understanding of key events leading to adverse outcomes for better predictions of toxicity.

00:49:16.000 --> 00:49:23.000
Um, as I mentioned at the beginning, early on, one of our goals is to use our 3D respiratory model to establish.

00:49:23.000 --> 00:49:36.000
Quantitative relationship between chemical exposure. and toxicity and make comparisons between our cell model and tissues from an in vivo system. So, in collaboration with Jordan Smith.

00:49:36.000 --> 00:49:41.000
In the predictive metabolism and dosimetry core at the Pacific Northwest National Lab.

00:49:41.000 --> 00:49:47.000
We've developed a dosimetry, or physiologically based pharmacokinetic model.

00:49:47.000 --> 00:49:52.000
to improve our ability to translate between endpoints that we measure in vitro.

00:49:52.000 --> 00:49:56.000
Um, to toxicity or health outcomes that can occur in humans.

00:49:56.000 --> 00:50:04.000
So, historically, PBPK models have been utilized in what's called a forward dosimetry approach.

00:50:04.000 --> 00:50:08.000
Uh, to predict tissue concentrations from human exposure doses.

00:50:08.000 --> 00:50:15.000
for use in extrapolating to animal studies. But in our studies, we want to use the PVPK model.

00:50:15.000 --> 00:50:22.000
Uh, to develop a reverse dosimetry. Model for predicting human exposure concentrations.

00:50:22.000 --> 00:50:29.000
from in vitro data, with the idea that concentrations that cause toxicity in cells.

00:50:29.000 --> 00:50:35.000
would then mimic concentrations at the tissue level.

00:50:35.000 --> 00:50:46.000
So to do this, uh, we need to collect data in our model on the disposition and metabolism of pHs within our culture system.

00:50:46.000 --> 00:50:51.000
And so I was going to spend some time walking through, um, our efforts to do this.

00:50:51.000 --> 00:50:59.000
Uh, we had broken our model down into compartments, um, with the goal to quantify metabolism and distribution.

00:50:59.000 --> 00:51:04.000
Um, across dose and time, and develop parameters for the dosimetry model.

00:51:04.000 --> 00:51:11.000
So our fractions reflect the mucous apical compartment, the cells, the media or plasma compartment.

00:51:11.000 --> 00:51:20.000
And then we also wanted to evaluate potential loss of pHs that may bind to plastic material.

00:51:20.000 --> 00:51:30.000
We developed the model, um, using the pH benzoate, um, just as a reference chemical, also because we do have a lot of information about benzoepyrine and.

00:51:30.000 --> 00:51:40.000
and knowledge about its metabolites and standards for those metabolites, so… Um, we use benzoepyrene to develop.

00:51:40.000 --> 00:51:45.000
parameters, um… To collect parameters, actually, for developing essentially two models.

00:51:45.000 --> 00:51:51.000
A model to describe the parent chemical, um, benzoid pyrine itself, and how it moves within.

00:51:51.000 --> 00:52:00.000
our system, and then also develop a model describing formation of metabolites, particularly those that contribute to the formation.

00:52:00.000 --> 00:52:14.000
of the dial epoxide leading to DNA damage. So before, uh, looking at the metabolite data, we first tracked how benzoypirine moved in our culture system between compartments.

00:52:14.000 --> 00:52:22.000
Um, across multiple time points, up to 48 hours after exposure. Uh, we were able to recover.

00:52:22.000 --> 00:52:28.000
Um, approximately 100% of benzoapyrine that was put into the system.

00:52:28.000 --> 00:52:36.000
And we see the amount of benzoipyrene then decrease over time, as we would expect metabolites to form.

00:52:36.000 --> 00:52:43.000
So, uh, when we looked at. benzoyapyrine in each compartment, we can see that benzoipyrene, um.

00:52:43.000 --> 00:52:55.000
We'll leave the mucous apical compartment over time. Um, we can see it moving into the cells, um, up to 4 hours before, um, also decreasing.

00:52:55.000 --> 00:53:12.000
And we see some benzoe pyrene moving into the media, but if you look at the y-axis, um, you can tell that this is much lower… at much lower levels than where, um, measuring benzoid pyrine in the other compartments. So actually very little of the parent benzoepyrine itself is moving into the.

00:53:12.000 --> 00:53:30.000
media fraction. We also really, um, were not able to, um… Identify benzoipyrine bound to plastic and so, um, this did not serve as a significant source of loss for benzoypine from our system.

00:53:30.000 --> 00:53:35.000
So to measure metabolite formation, we also collected samples.

00:53:35.000 --> 00:53:43.000
Uh, multiple time points up to 48 hours for extraction and analysis by UPLC with fluorescence detection.

00:53:43.000 --> 00:53:54.000
So this is a schematic for benzoypirine metabolism. We see benzoipyrene here in the center, and different metabolites that can form, um, through.

00:53:54.000 --> 00:54:01.000
Uh, various pathways. So while we aren't able to quantify all of the metabolites.

00:54:01.000 --> 00:54:09.000
We can quantify many of them that we, um, have standards for, and so those are listed here.

00:54:09.000 --> 00:54:17.000
And out of those metabolites, we were primarily able to detect these 6 metabolites that are, um.

00:54:17.000 --> 00:54:22.000
highlighted in red, and we can see from the UPLC trace, um.

00:54:22.000 --> 00:54:35.000
the peaks for these metabolites. Uh, so this includes a number of metabolites, but particularly, as I mentioned, we were interested in those associated with the formation of.

00:54:35.000 --> 00:54:45.000
Um, the dial epoxide, benzoepyrine 7-8, diol 910 epoxide, um, that can interact with DNA and cause DNA damage.

00:54:45.000 --> 00:54:55.000
So, uh, we were able… while we can't… Uh, measure the dial epoxide itself. Due to stability, we can measure, um, metabolites upstream.

00:54:55.000 --> 00:55:03.000
Um, so we can measure the 7-8. Diol, and also the tetraols downstream.

00:55:03.000 --> 00:55:17.000
So after we look at formation of metabolites. Over time, we can see, um… formation of a number of metabolites, and I'm just going to highlight an increase in the 7-8 diol in blue.

00:55:17.000 --> 00:55:23.000
Um, and an increase in the tetrals in red, um, that are formed over time.

00:55:23.000 --> 00:55:29.000
Um, and again, these are upstream and downstream of the dial epoxide.

00:55:29.000 --> 00:55:34.000
We also see that, um, metabolites account for the majority.

00:55:34.000 --> 00:55:41.000
Of benzo a pyrene that's recovered at later time points. So, we start to, um.

00:55:41.000 --> 00:55:50.000
Really see measurable… uh, metabolites, um, contributing to total recovery at 8 hours, and then this contributes to a majority.

00:55:50.000 --> 00:55:55.000
of the metabolites that are formed. Um, at the later time points.

00:55:55.000 --> 00:56:00.000
So while, uh… detection of these metabolites.

00:56:00.000 --> 00:56:05.000
indicate that we are likely generating the dial epoxide itself, leading to DNA damage.

00:56:05.000 --> 00:56:10.000
Uh, we did also evaluate DNA damage in cells.

00:56:10.000 --> 00:56:16.000
After treatment, um, using a comment-based assay, um, in collaboration.

00:56:16.000 --> 00:56:24.000
with Bevin Englewart's lab at MIT. Uh, this assay detects single-strand breaks mediated by genotoxic intermediates.

00:56:24.000 --> 00:56:37.000
generated through metabolism of pHs. Um, this method uses trapping agents to block repair mechanisms, so damaged DNA can be viewed as comets, and you can see examples here of.

00:56:37.000 --> 00:56:45.000
undamaged DNA and DNA after treatment. So, using this assay, we were able to detect.

00:56:45.000 --> 00:56:55.000
Um, a dose-dependent increase in the DNA damage with benzoipyrene in the presence of trapping agents, which are here on the right-hand side.

00:56:55.000 --> 00:57:04.000
But not when, uh. trapping agents were not included in our negative controls, um, where we aren't able to.

00:57:04.000 --> 00:57:15.000
Um, observe significant DNA damage after benzoypirine treatment. So this exit, um, suggests that the damage that we were seeing, uh, was mediated by generation of these reactive.

00:57:15.000 --> 00:57:29.000
intermediates, um, of pH metabolism. Um, so we were… we were observing DNA damage at 24 hours. Um, this correlates, uh, with formation of the Phase I metabolites.

00:57:29.000 --> 00:57:33.000
Um, which are quantified in bulk here in blue.

00:57:33.000 --> 00:57:42.000
Um, and we start to see, again, significant, um, formation of metabolites in 8 hours that peak at 24 hours.

00:57:42.000 --> 00:57:49.000
This also correlates with induction of CYP1A1 enzyme activity in our cells, which is the black line.

00:57:49.000 --> 00:57:53.000
Um, which we see peak at approximately 6 to 8 hours.

00:57:53.000 --> 00:58:03.000
Um, after treatment. And CYP11 is one of the primary enzymes responsible for pH metabolism in lung cells.

00:58:03.000 --> 00:58:10.000
I will also mention that, um, we did see evidence of Phase II metabolism by glucuronides in our cells.

00:58:10.000 --> 00:58:16.000
Uh, so if we incubate our samples with glucuronidase to inhibit metabolism.

00:58:16.000 --> 00:58:23.000
We saw approximately 50% increase in measurable phase 1 metabolites at the 24 to 48.

00:58:23.000 --> 00:58:32.000
our time points, um, improving our overall recovery. Of, um, total BAP added to the system at these time points.

00:58:32.000 --> 00:58:42.000
We are continuing to, uh, still investigate, uh, where the rest of the total mass may be at these time points.

00:58:42.000 --> 00:58:53.000
just based on total recovery of what's put into the system, but it is likely… Uh, much of it is likely due to a combination of, um, Phase I metabolite peaks.

00:58:53.000 --> 00:59:04.000
Um, that we haven't identified yet. Uh, or other Phase 2 metabolite processes besides glucuronidation.

00:59:04.000 --> 00:59:10.000
So we use this data to, um, first build a diff symmetry model for the parent chemical benzoapyrine.

00:59:10.000 --> 00:59:17.000
Um, by calculating parameters for absorption, permeation through cells, partitioning into media.

00:59:17.000 --> 00:59:33.000
Elimination processes of metabolism and volatilization. Um, when we overlay our predicted or simulated model, which are the, um, represented by the lines onto our actual measurements, um, that were collected from ourselves.

00:59:33.000 --> 00:59:38.000
Which are the dots. We do see that we have a very good fit.

00:59:38.000 --> 00:59:45.000
of the model to our data. So, in red, we see prediction of, um, benzoe pyrene in the media.

00:59:45.000 --> 00:59:52.000
although is, um… we presented very little of the parent itself is, um, moving into the media.

00:59:52.000 --> 00:59:58.000
In Black, uh, we see, um, prediction of benzoipyrine in cells.

00:59:58.000 --> 01:00:02.000
And in blue, we see prediction of metabolite formation.

01:00:02.000 --> 01:00:08.000
And so, as I mentioned, while we can't account for all of the potential metabolism that's occurring.

01:00:08.000 --> 01:00:14.000
Um, our model accounts for at least the minimum amount of metabolism achieved.

01:00:14.000 --> 01:00:26.000
And so, um, and I'll note that. Um, well, we start to see significant metabolites at 8 hours, metabolites do begin to appear at approximately 4 hours.

01:00:26.000 --> 01:00:40.000
So we can incorporate, um, metabolite formation into the model using a very similar, um, using similar parameters that we did for the parent itself. So, calculating parameters for formation of the metabolite, permeation through cells.

01:00:40.000 --> 01:00:48.000
partitioning into mucus, as well as active transport into other, um, compartments, and elimination of.

01:00:48.000 --> 01:00:53.000
Um, metabolites. my metabolism and volatilization.

01:00:53.000 --> 01:01:01.000
So, combined, uh, this provides, uh. pharmacokinetic model for benzoipyrene in our cell system.

01:01:01.000 --> 01:01:13.000
Accounting for how cells move throughout the system and how they are quantified in a… how they are metabolized in a quantitative manner.

01:01:13.000 --> 01:01:23.000
In addition to developing a dosimetry model, um. This effort also helped us to establish a better understanding of the metabolic.

01:01:23.000 --> 01:01:28.000
competency of, um… our ALI model.

01:01:28.000 --> 01:01:37.000
And… This can help us improve our ability to predict toxicity down the line.

01:01:37.000 --> 01:01:42.000
So we're currently working to expand our assessment of, um.

01:01:42.000 --> 01:01:48.000
dosimetry to other PAHs besides benzoapyrine, so that we can start to make.

01:01:48.000 --> 01:01:57.000
predictions for movement and metabolism. of pHs with different chemistries, um… in our 3D model, and see if we can.

01:01:57.000 --> 01:02:05.000
predict based on chemistry, um… what might be happening to chemicals within our culture system.

01:02:05.000 --> 01:02:15.000
Ultimately, uh, what we would like to do with this data is apply it for in vitro to in vivo extrapolation so that we can translate toxicity, um.

01:02:15.000 --> 01:02:29.000
that we're observing in our in vitro systems. to in vivo systems, and then… associate concentrations that cause toxicity in vitro with those that are being measured as part of our broader program through passive sampling.

01:02:29.000 --> 01:02:38.000
Um, and concentrations that we know individuals are exposed to in the environment.

01:02:38.000 --> 01:02:45.000
Um, as I mentioned earlier, we're also modifying our, um, ALI model to just.

01:02:45.000 --> 01:02:51.000
to study disease phenotypes and generate co-culture, so I just wanted to spend a few minutes, um.

01:02:51.000 --> 01:03:05.000
talking about some of these efforts fairly briefly, so… Um, we can induce disease phenotypes during differentiation, and we're currently working with an asthmatic phenotype where cells are differentiated in the.

01:03:05.000 --> 01:03:10.000
The presence of interleukin-13 over 14 days to generate a phenotype.

01:03:10.000 --> 01:03:18.000
We're the pathophysiology is similar to what's reported in individuals with type 2 allergic asthma, and so this is.

01:03:18.000 --> 01:03:30.000
been evaluated by us and by others in the literature, um… with the phenotype exhibiting mucociliary dysfunction, airway remodeling, mucous hypersecretion, and.

01:03:30.000 --> 01:03:38.000
And also loss of barrier integrity. So we're interested to understand these cumulative risks to public health from combined stressors.

01:03:38.000 --> 01:03:46.000
Um, recent animal models have identified pulmonary inflammation from respiratory disease, such as asthma as a possible modifier, and.

01:03:46.000 --> 01:03:54.000
And, um, risk factor for chemical toxicity in the lung after exposure to inhaled pollutants.

01:03:54.000 --> 01:04:04.000
Um, overall, asthma affects. 8% of the US population and more than 260 million people worldwide. Um, in our state, Oregon ranks 5th.

01:04:04.000 --> 01:04:08.000
Um, out of all states in asthma incidents overall.

01:04:08.000 --> 01:04:21.000
So rates of asthma in our state, um. do exceed the national average, um, range between 9 and 13%, and it's particularly relevant for communities adjacent to the Portland Harbor Superfund site.

01:04:21.000 --> 01:04:35.000
Which is highlighted here in gray. Um, so it makes them a unique and vulnerable population for subsequent chemical insults after respiratory exposure to inhaled chemicals from the Superfund site.

01:04:35.000 --> 01:04:41.000
So we have characterized our model in the presence, um, we've characterized the phenotype itself.

01:04:41.000 --> 01:04:50.000
Um, and can measure significant reduction in barrier integrity using transepithelial electrical resistance.

01:04:50.000 --> 01:04:58.000
We can also see increased detection of mucus and mucus-producing goblet cells in the phenotype itself.

01:04:58.000 --> 01:05:03.000
So, barrier integrity, uh. of the airway epithelium remains.

01:05:03.000 --> 01:05:23.000
Um, maintains homeostasis, uh, protects against environmental factors. Barrier dysfunction itself can increase risk of chemical uptake and also enhancement of chronic inflammation, so… Um, we have evaluated our, um, disease phenotype model in the presence of PAHs and.

01:05:23.000 --> 01:05:34.000
particular here, I'm showing some data with a mixture that contains primarily alkylated PAHs that was collected from air sampling at a creosote site during a wildfire event.

01:05:34.000 --> 01:05:44.000
Um, in our region. And, um, when we expose both the asthmatic phenotype and hash spars in normal cells and solid, um.

01:05:44.000 --> 01:05:50.000
to this mixture of pHs. We really only see, um, further reduction of barrier integrity.

01:05:50.000 --> 01:05:57.000
In the asthmatic phenotype, um. compared to normal cells, suggesting that.

01:05:57.000 --> 01:06:03.000
These individuals really may be more susceptible to chemical insult when compared to healthy individuals.

01:06:03.000 --> 01:06:15.000
Um, so we have, um, evaluated this through a number of ways, and using some global approaches, we… Um, know that as the asthmatic phenotype and lung cells in the asthmatic phenotype.

01:06:15.000 --> 01:06:25.000
Um, respond to PAHs, um. suggesting that they are… Causing toxicity through unique mechanisms in the disease model.

01:06:25.000 --> 01:06:33.000
Uh, we're continuing to explore how individuals with inflammation-based disease may respond differently to pH toxicity.

01:06:33.000 --> 01:06:42.000
And we're also doing this by utilizing a macrophage epithelial co-culture model to effectively evaluate immune contribution.

01:06:42.000 --> 01:06:53.000
Um, so… So one thing that we are exploring is, um, increasing the complexity of our culture system to better mimic in vivo studies.

01:06:53.000 --> 01:06:58.000
And, um, use this to help us evaluate some of these, um.

01:06:58.000 --> 01:07:02.000
highly abundant chemicals that we're able to measure, um.

01:07:02.000 --> 01:07:06.000
Associated with Superfund site, but also in wildfire smoke.

01:07:06.000 --> 01:07:10.000
Uh, we know that induction of airway inflammation is orchestrated.

01:07:10.000 --> 01:07:19.000
Uh, through signaling between airway epithelial cells. And macrophages, and so, um, the co-culture model incorporates, um.

01:07:19.000 --> 01:07:27.000
Macrophage cells into our 3D model, um, just as another way to expand the use of these 3D models to evaluate.

01:07:27.000 --> 01:07:32.000
the combined contribution of airway epithelial and macrophage cell communication.

01:07:32.000 --> 01:07:42.000
In terms of determining toxicity. So, in conclusion, I just, uh, want to emphasize the importance of utilizing.

01:07:42.000 --> 01:07:56.000
integrated approaches for understanding chemical toxicity. Uh, this has been important across our entire program and allows us to prioritize environmentally relevant chemicals and exposures for testing and filling critical data gaps for these.

01:07:56.000 --> 01:08:06.000
Understudied and undermeasured chemicals. Um, even within a class of what we would typically consider to be very well-studied polycyclic aromatic hydrocarbons.

01:08:06.000 --> 01:08:09.000
Um, there exist a lot of… a lot of data gaps.

01:08:09.000 --> 01:08:15.000
Uh, there are benefits to using cell-based NAMs combined within silico approaches to improve.

01:08:15.000 --> 01:08:24.000
Our ability to translate studies from in vitro to in vivo outcomes based on quantitative understanding of dosing and pharmacokinetics on our system.

01:08:24.000 --> 01:08:32.000
We can also use these tools to improve our understanding of susceptibility due to combined stressors like pre-existing disease.

01:08:32.000 --> 01:08:39.000
Um, that are common in target populations near relevant exposure sources, like the Portland Harbor Superfund site.

01:08:39.000 --> 01:08:47.000
Um, future studies in our, um, we are really interested in continuing to understand mechanisms of toxicity for alkyl pHs.

01:08:47.000 --> 01:09:03.000
Um, including self-specific responses, um. in our lung culture model and in our co-culture model. Um, so… As Steven mentioned, we also see less sensitivity in our 3D model.

01:09:03.000 --> 01:09:25.000
in response to pHs, like benzoypirine and others. You know, for broad endpoints like cytotoxicity, but for also specific endpoints, like DNA damage and SYP induction. And, um… We have some evidence that, um, this is likely due to differential response across the different cell types in the 3D model, and so we're continuing to explore that more.

01:09:25.000 --> 01:09:30.000
Um, as well as look at sources of variants that could contribute to inter-individual response.

01:09:30.000 --> 01:09:38.000
Um, to toxicity. So with that, I just want to thank, um, all of the.

01:09:38.000 --> 01:09:48.000
Um, past and current contributors. Uh, to all of this work, uh, within my group, and also our collaborators within the Superfund program.

01:09:48.000 --> 01:09:54.000
And outside of the Superfund program, as well as our funding sources.

01:09:54.000 --> 01:10:00.000
And, uh, with that, I thank you and can take, uh, questions.

01:10:00.000 --> 01:10:05.000
Okay, thank you for the presentation, Susan. It was excellent.

01:10:05.000 --> 01:10:10.000
Um, so we have several questions here in the question and answer box.

01:10:10.000 --> 01:10:13.000
We'll probably only be able to get through a few here.

01:10:13.000 --> 01:10:19.000
Um, versus, can you please comment on the confidence in separating the mucus fraction versus media?

01:10:19.000 --> 01:10:26.000
Or cells in the ALI model.

01:10:26.000 --> 01:10:36.000
Um… so… When we are collecting, um, the mucus, we are using… we are essentially.

01:10:36.000 --> 01:10:45.000
We're regularly washing the cells, um. generally weekly during differentiation, and so we use a similar process of.

01:10:45.000 --> 01:10:51.000
Um, washing the cells in terms of collecting the mucus fraction.

01:10:51.000 --> 01:11:00.000
Um, compared to collecting our cellular fraction. So there is possibly, you know, some overlap in that.

01:11:00.000 --> 01:11:04.000
in that collection process.

01:11:04.000 --> 01:11:10.000
Okay, so next question for benzoepyrine. Well, you didn't recover much from plastic.

01:11:10.000 --> 01:11:18.000
Did the amount measured in other compartments represent the most of the initial exposure added to the system?

01:11:18.000 --> 01:11:30.000
Yes, we were able to, um… we did go through and look at a mass balance, and we were able to account for essentially 100% of the mass that was put into the system, and.

01:11:30.000 --> 01:11:41.000
It's when we get to the later time points where we know we're having metabolism, and we're accounting for some of those metabolites with, um, the standards that we have.

01:11:41.000 --> 01:11:58.000
Um, and there are, um… those later time points where we still are working to identify additional metabolites that might be contributing to that total mass, but certainly for the majority of the time course.

01:11:58.000 --> 01:12:09.000
We can account for, uh, definitely benzoate pyrine, and even benzo pyrine in combination with metabolites, um, is a majority of what's been added to the system.

01:12:09.000 --> 01:12:22.000
Okay, so we have time for one more question. The PK modeling in vitro is a major advance. Thank you. Can you comment on how this model and data is helping to bridge in vitro and in vivo situations?

01:12:22.000 --> 01:12:29.000
In other words, what is the benefit of this very involved work in human risk assessment?

01:12:29.000 --> 01:12:37.000
So, um, one thing that we really want to be able to do is start to make predictions in our system about.

01:12:37.000 --> 01:12:48.000
Um, chemicals with different chemistries. how we can predict how they move within our system, um, how they're metabolized, and at what rates, um.

01:12:48.000 --> 01:12:57.000
at what rates they're metabolized, how that is linked to, um, specific endpoints in our lung cell system.

01:12:57.000 --> 01:13:06.000
So that we can start to identify threshold concentrations that cause toxicity, and then make very specific, more quantitative comparisons to.

01:13:06.000 --> 01:13:16.000
how the concentration in vitro, um, is then. Um, link to potential exposure concentrations where.

01:13:16.000 --> 01:13:28.000
We know we have, um… Our collaborators are in the field with passive samplers, um, measuring chemicals in the environment. We know what these exposure concentrations are, and so we'd like to be able.

01:13:28.000 --> 01:13:34.000
To start to prioritize some of our studies, um, based on both what we're seeing in terms of toxicity.

01:13:34.000 --> 01:13:47.000
But also, combined with, um, the exposure concentrations for what we know are, um, most abundant and most important in these mixtures.

01:13:47.000 --> 01:13:50.000
Well, thank you very much, Susan. We appreciate it.

01:13:50.000 --> 01:14:02.000
So, our final speaker today is Aram Hahn, a professor in the Department of Electrical and Computer Engineering and Biomedical Engineering at Texas A&M University.

01:14:02.000 --> 01:14:06.000
He is also faculty with the Texas A&M Health Science Center.

01:14:06.000 --> 01:14:13.000
and the Texas A&M Institute for Neuroscience. His research interests are in solving grand challenge problems.

01:14:13.000 --> 01:14:19.000
and the broad areas of health and energy through the use of micro and nanosystem technologies.

01:14:19.000 --> 01:14:24.000
Dr. Han will discuss the fetal-maternal interface tissue chip.

01:14:24.000 --> 01:14:28.000
to study the effect of environmental substances on preterm birth.

01:14:28.000 --> 01:14:32.000
So, Dr. Hahn, I'll turn it over to you.

01:14:32.000 --> 01:14:41.000
Thank you. Um… I guess for some reason, I don't see the, uh, share screen button, so I guess somebody from the NIHSI.

01:14:41.000 --> 01:14:49.000
Could maybe just a share. the presentation.

01:14:49.000 --> 01:14:54.000
Thank you, appreciate it. So, uh, my name is Arum Khan, I'm a faculty at Texas A&M University.

01:14:54.000 --> 01:15:06.000
I'm going to talk about organoid chip models of the fetal motor interface, enabling rapid hazard analysis of environmental contaminants impacting pregnancy. Next slide.

01:15:06.000 --> 01:15:10.000
So… I've been collaborating with colleagues.

01:15:10.000 --> 01:15:16.000
Uh, we're very much interest in looking into preterm birth and the adverse pregnancy outcome.

01:15:16.000 --> 01:15:25.000
Um, this just shows the global preterm birth rate, where unfortunately, we have 150 million babies born prematurely in the last decade.

01:15:25.000 --> 01:15:31.000
And our worldwide preterm birth rate, about 11% of all of the pregnancy.

01:15:31.000 --> 01:15:44.000
Next. And, uh, so there's a strong need to understand the mechanism, identify high-risk pregnant subjects, and provide proper intervention, which is very much lacking. Next.

01:15:44.000 --> 01:15:53.000
So, uh, if you look at the preterm birth, it has a fairly complex etiology. Some of the preterm birth is caused by infection-associated inflammation.

01:15:53.000 --> 01:15:59.000
relatively easily identifiable, and that's about 40% of the preterm birth, but the rest of them.

01:15:59.000 --> 01:16:04.000
is due to variety different risk factor induced by non-infectious inflammation.

01:16:04.000 --> 01:16:08.000
The cause of this non-infectious inflammation could vary a lot.

01:16:08.000 --> 01:16:12.000
And that really, uh, makes it very difficult to study this one.

01:16:12.000 --> 01:16:17.000
Where this inflammation compromises… once it compromises the fetal motor interface.

01:16:17.000 --> 01:16:30.000
that could trigger the pretembrance pathway. Next. So, we… our team, in collaboration, uh, all of this work has been in collaboration with Dr. Ramku Menon.

01:16:30.000 --> 01:16:34.000
A professor in obstetric and gynecology, University of Texas Medical Branch in Galveston.

01:16:34.000 --> 01:16:44.000
And together in the past 6-7 years, together with Dr. Menon, we have been working on developing a variety of different NPS models of the female reproductive tract.

01:16:44.000 --> 01:16:49.000
We initially, our initial work was started out with the M9 membrane organ chip.

01:16:49.000 --> 01:16:55.000
In advance, it had some technical advancement, built into fetal material fetal membrane over a chair.

01:16:55.000 --> 01:17:03.000
And then, uh, we developed a variety of different ownership with the goal of really understanding the entirety of the female reproductive tech.

01:17:03.000 --> 01:17:11.000
track, uh, both from mechanistic understanding as well as a variety of different factors that may impact female reproduction.

01:17:11.000 --> 01:17:24.000
Next. So, um, amongst all variety of different organ systems, uh, today I would like to really focus on the fetal maternal interface and the complex nature of this interface.

01:17:24.000 --> 01:17:30.000
If you look at the fetal motor interface, in other words, the entire interface that surrounds the fetus.

01:17:30.000 --> 01:17:37.000
There are two different interfaces. One is the placental interface, which is probably most well studied.

01:17:37.000 --> 01:17:41.000
And the other one is the fetal fetal membrane interface.

01:17:41.000 --> 01:17:47.000
And each of these interfaces are composed of multiple complex layers. Next.

01:17:47.000 --> 01:17:57.000
So, if you look at the… challenge of current models to study the fetal-maternal interface, there are many challenges that are very similar to any other organ system.

01:17:57.000 --> 01:18:02.000
Where 2D culture explains human cell cultures have a variety of different limitations.

01:18:02.000 --> 01:18:08.000
animal models such as mouse models also have a variety of different limitations.

01:18:08.000 --> 01:18:18.000
However, for pregnancy-specific animal model poses additional challenge because the pregnancy, for example, the pregnancy mouse is very different from pregnancy in human.

01:18:18.000 --> 01:18:22.000
So, a much bigger difference to some degree compared to other organ systems.

01:18:22.000 --> 01:18:33.000
And, uh, non-human primate, probably the most, uh, mimicking in terms of human pregnancy, but doing studies using non-human primate really, uh, in terms of cost, uh, in terms of cost.

01:18:33.000 --> 01:18:42.000
is really not a routinely usable tool. Explained perfusion studies at term placenta have been utilized, but there are also somewhat limited.

01:18:42.000 --> 01:18:52.000
Next. So, we've been working on, uh, developing a chip system for the fetal membrane, specifically.

01:18:52.000 --> 01:18:59.000
A lot of initial work was enabled by two, uh, funding, one from, from an NICHD.

01:18:59.000 --> 01:19:06.000
are one that studies intercellular injection that defines cell migration and transition, maintaining field membrane homeostasis.

01:19:06.000 --> 01:19:14.000
was really using, developing a, uh. and PS system of a fetal membrane and utilize this one to study a variety of different mechanisms.

01:19:14.000 --> 01:19:19.000
The other one is the clinical trial part of the NCAS clinical trial and CHIP.

01:19:19.000 --> 01:19:24.000
Where we are one of the 10 teams that, uh, received funding.

01:19:24.000 --> 01:19:34.000
It was a joint NCIS NICHD funding to look to develop a maternal-fetal interphase on a chip and use it to generate preclinical data.

01:19:34.000 --> 01:19:45.000
Next. So, if I'm focusing on the fetal, uh, fetal maternal interface, as I mentioned, we are looking into two interfaces.

01:19:45.000 --> 01:19:52.000
One is the fetal membrane, the other one is the placental interface, and each of them are composed of multiple different cellular layer.

01:19:52.000 --> 01:20:04.000
Next. And so, uh, we have developed a field member on a chip. We focus on 4 different cell types, uh, one maternal cell type, three different fetal cell type.

01:20:04.000 --> 01:20:10.000
I'm gonna go into this particular design configuration a little bit more in detail in a later slide.

01:20:10.000 --> 01:20:15.000
But basically, it's a full concentric ring structure of silica compartment.

01:20:15.000 --> 01:20:21.000
connected by Aria for Microfluid channel, and so basically a 4-cell type cochlear system.

01:20:21.000 --> 01:20:35.000
Next, the placental, uh, placenta interface organ chair. focusing on 3 different cell types, and it is a rectangular-shaped co-culture chamber, organically connected by OSF of a microfluid channel.

01:20:35.000 --> 01:20:45.000
So these two have been our main ownership of the fetal maternal interface that we have developed and have been utilizing for a variety of different studies.

01:20:45.000 --> 01:20:51.000
Next. So if you look at the basic key features of our particular MPS model.

01:20:51.000 --> 01:20:58.000
And there are typically a vertical co-culture model, and there are horizontal co-culture model.

01:20:58.000 --> 01:21:03.000
In our case, the basic configuration is basically a horizontal co-code model.

01:21:03.000 --> 01:21:08.000
We have two, in this case, in this example, we have two different cell culture compartments.

01:21:08.000 --> 01:21:14.000
connected by RAF microfluid channel. So these smoker fluke channels are small enough that prevents.

01:21:14.000 --> 01:21:19.000
Passive, uh, movement of cells from one compartment to another compartment.

01:21:19.000 --> 01:21:27.000
In other words, when you load the cell into cell chamber A, they don't simply flow into cell chamber B, so that we can keep them separate.

01:21:27.000 --> 01:21:35.000
However, they are large enough to allow any biochemicals to transition or diffuse from one chamber to the other one.

01:21:35.000 --> 01:21:41.000
Uh, so these are a variety of different cell-produced factors as well as the toxicant that we would like to apply.

01:21:41.000 --> 01:21:49.000
Um, so this is a two-chamber example, and these channels, depending on what particular part of the fetal membrane we would like to mimic.

01:21:49.000 --> 01:21:59.000
These channels can be actually filled with extracellular matrix, so on the lower right side, you will see a scanning electron microscope image of a microfluid channel.

01:21:59.000 --> 01:22:03.000
filled with collagen in this case, so we have already of this channel.

01:22:03.000 --> 01:22:10.000
And the main reason, one of the main reasons we use this horizontal co-culture configuration is it allows imaging very easy.

01:22:10.000 --> 01:22:14.000
And we can simply expand the number of different cocaine chamber.

01:22:14.000 --> 01:22:22.000
Versus the vertical co-culture configuration usually limited to a, uh, two-chain… two-cell type co-culture.

01:22:22.000 --> 01:22:35.000
Next, uh, the second key feature is we have, um… sorry, so we have a localized cell loading, cell migration, biochemical diffusion, all of these key functions enabled by this device.

01:22:35.000 --> 01:22:42.000
The next slide shows the, uh, the second feature where we have a media reservoir sitting on top of their main culture chamber.

01:22:42.000 --> 01:22:46.000
So basically, we have a plastics sitting on top of this, they are bonded together.

01:22:46.000 --> 01:22:54.000
And if you look at the next slide, we will… will it basically have a gradient-driven media diffusion.

01:22:54.000 --> 01:23:00.000
And that enables localized media supply, localized effluent collection, and as well as localized treatment.

01:23:00.000 --> 01:23:08.000
So, whatever factors that are produced by cells, they will be diffused into media compartment, so that we can sample those.

01:23:08.000 --> 01:23:13.000
When we are applying a tox scan, which I'm going to show later on, we can apply to one chamber.

01:23:13.000 --> 01:23:20.000
Uh, and then that Toxic gun can, depending on the situation, that Tox gun can diffuse from one chamber to another chamber.

01:23:20.000 --> 01:23:25.000
So we can use this media reservo block to do, uh, to enable this one.

01:23:25.000 --> 01:23:34.000
So here, uh, roughly the size of this initial device fits in a well over a 6-wheel chamber. Next.

01:23:34.000 --> 01:23:43.000
So, in terms of cell source, um, cell source are one of the most challenging parts of any NPS devices. In many cases, people are using IPSC.

01:23:43.000 --> 01:23:49.000
In the case of a MPS mouse of the phylumatin interface, there are really no IPAs available.

01:23:49.000 --> 01:23:58.000
So, what we do is we, uh, initially, about 6-7 years ago, when we initially started this project, we used primary cells harvested from.

01:23:58.000 --> 01:24:03.000
Uh, just got it, uh, placental tissue from a thrombus.

01:24:03.000 --> 01:24:12.000
The past several years, my colleagues, Dr. Menon's group has now made this immortalized this one and developed this one into a cell line.

01:24:12.000 --> 01:24:19.000
have done a variety of different testing to show that these cell lines are very robust, so now we have a robust supply of a different.

01:24:19.000 --> 01:24:29.000
cell lines derived from primary cells. And, uh, which we are currently using in all of our, uh, different, uh, MPS devices of the female reproductive system.

01:24:29.000 --> 01:24:44.000
Next. So, um, several years ago, um, I started looking into where, beyond, let's say, a mechanistic study, beyond drug discovery.

01:24:44.000 --> 01:24:52.000
Where we can utilize it. And so, in the past several years, I really had a great pleasure of working as part of the Texas A&M Super Fund Research Center.

01:24:52.000 --> 01:25:00.000
This is 2022 is where the renewal started. And so I participated as a Project 3.

01:25:00.000 --> 01:25:11.000
Um, so first of all, the overall goal of the A&M Super Fundraising Center is comprehensive tools and models for addressing exposure to mixture during environmental emergency-related contaminant event.

01:25:11.000 --> 01:25:19.000
So, two things. One is focus on mixture. Second one is focusing on emergency, environmental emergency-related contaminant event.

01:25:19.000 --> 01:25:26.000
So, within that context, we looked into the pregnant woman as one of the vulnerable population.

01:25:26.000 --> 01:25:33.000
And Product C is trying to address that, and here you see a center overview where we have 5 different projects and many different core.

01:25:33.000 --> 01:25:40.000
So the project tree that really utilizes the freedom interface, or on a chip system.

01:25:40.000 --> 01:25:46.000
working very closely with many of the center component to look into the potential hazard of.

01:25:46.000 --> 01:25:58.000
individual chemical and mixture. Uh, especially coming from environmental emergency-related contaminant, and how that may impact the pregnancy and potentially associated with pretembrance.

01:25:58.000 --> 01:26:11.000
Next. So, it's the very first study at the early stage of this project, we have, uh, we have used a very well-known, uh, contaminant, uh, cadmium.

01:26:11.000 --> 01:26:14.000
There's been a bunch of etiological studies out there.

01:26:14.000 --> 01:26:22.000
So, we're using this 4-chamber fetal motor interface device. We basically apply cadmium into the maternal chamber and looked at how.

01:26:22.000 --> 01:26:32.000
cadmium transport from the maternal chamber to the 3 different layers of the fetal chamber, so we can look into propagation.

01:26:32.000 --> 01:26:38.000
And most importantly, we can look at ads academy propagates through the different cellulaya.

01:26:38.000 --> 01:26:44.000
Which you can sort of see in the illustration, what I see in the figure C here, inflammatory response.

01:26:44.000 --> 01:26:49.000
We can look at how the different inflammation and cell death responding to.

01:26:49.000 --> 01:26:56.000
to as can even propagate. So, as ketamine propagate from the lower side, which is the maternal descendior chamber.

01:26:56.000 --> 01:27:01.000
to the upper side, to a different fetal layer, we can look in how a cell does occur.

01:27:01.000 --> 01:27:08.000
how inflammation occurred, so this allows, this shows that this fetal maternal interface ownership.

01:27:08.000 --> 01:27:17.000
can assess chemical transport kinetics using this device. And then, uh, also look into toxic and exposure-mediated adverse effect at the fetal maternal interface.

01:27:17.000 --> 01:27:23.000
And so here we can see both direct result coming from a direct exposure to caladium.

01:27:23.000 --> 01:27:28.000
As well as indirect exposure coming from other factors or other inflammatory factors.

01:27:28.000 --> 01:27:32.000
That are diffusing from. one cellular layer to another layer.

01:27:32.000 --> 01:27:42.000
Next. So… If I'm looking at the microphysical system, which, uh, which sometimes people call organoid shape or tissue shape.

01:27:42.000 --> 01:27:50.000
Uh, as I sort of… shown partially, and you alluded to, there are many unique features why people are using this MP system.

01:27:50.000 --> 01:27:57.000
essentially more in vivo-like in vitro system can control the cellular microenvironment very well.

01:27:57.000 --> 01:28:02.000
Can co-culture multiple different cell types in a tightly controlled manner.

01:28:02.000 --> 01:28:08.000
Uh, in three-dimensional or 2.5D. depending on how the in vivo situation is.

01:28:08.000 --> 01:28:15.000
My Costco… my cost could be comparable, and we also can be integrated with a variety of different feature… a sensor.

01:28:15.000 --> 01:28:22.000
However, next, however, if you look at, uh, whether we can use them as a routine to learn model.

01:28:22.000 --> 01:28:26.000
There are many challenges that we need to overcome. Next.

01:28:26.000 --> 01:28:32.000
So, some of the challenges are it require, oftentimes, not always, but oftentimes require.

01:28:32.000 --> 01:28:46.000
dedicated, uh, tool and instrument. Uh, to be able to use this MPS device, and sometimes doesn't really compare… is not really comparable with a traditional, uh, workflow in a lot of.

01:28:46.000 --> 01:28:59.000
medical lab, user-friendliness, relatively low, and uh. Some, like, most importantly, throughput, whether it's a fabrication, throughput, operation of throughput, that throughput is relatively known.

01:28:59.000 --> 01:29:10.000
low. So, as I work with my colleague in the Superfund Center that is led by Dr. Ivan Rusin here in the vet school at A&M.

01:29:10.000 --> 01:29:16.000
You know, by the time you have a couple different replicates, couple different dose response, positive control.

01:29:16.000 --> 01:29:24.000
Even for a single chemical, uh, chemical toxicon, the number of experiments that you have to run easily in the several tens of.

01:29:24.000 --> 01:29:31.000
So, next slide. Well, we're really looking to, can we really improve this one? So, if you look at the next slide.

01:29:31.000 --> 01:29:36.000
Uh, we have been working on increasing throughput to improve the MPH utility.

01:29:36.000 --> 01:29:42.000
So, in an example of our two-chamber unit, uh, which.

01:29:42.000 --> 01:29:51.000
Uh, we look into both from fabrication side as well as operations side. So, if you look at the fabrication side, initially, this is all a.

01:29:51.000 --> 01:30:05.000
Microfabrication process. Uh, called Replica molding. So we have a master mold from which you are replica molding a variety of different polymer devices. So, in a simple step is we went from a 4-inch.

01:30:05.000 --> 01:30:13.000
way for Massimold into 6-inch wafer mode, so that in a single fabrication run, we can fabricate many more devices easily.

01:30:13.000 --> 01:30:25.000
Um, and then in going from a putting individual devices, uh, into a 6-wheel, well over 6-wheel device, we created some custom devices so that we can have an operational improvement.

01:30:25.000 --> 01:30:36.000
Especially in terms of device configuration. So that way it fits in a conventional standard plate assay format for higher throughput operation.

01:30:36.000 --> 01:30:42.000
Next, in a second example, this is how we configured our 4-chamber order chip device.

01:30:42.000 --> 01:30:47.000
Obviously, the fourth chamber device require a little bit more larger footprint.

01:30:47.000 --> 01:30:59.000
Uh, so we modify the device configuration a little bit so that we can still fit many of these full chamber, full cochle chamber device into a plate format.

01:30:59.000 --> 01:31:09.000
So here, each of the individual array has 5 independent devices, and we configure this one so that 4 of these array fits in a standard, uh.

01:31:09.000 --> 01:31:15.000
96 world plate format. So, we worked on some design optimization and geometry.

01:31:15.000 --> 01:31:21.000
to really be able to fit this one, to make not only a fabrication process easier, but.

01:31:21.000 --> 01:31:24.000
The operation price is also easier. Next.

01:31:24.000 --> 01:31:30.000
So, then, uh, we also wanted to adopt this one to an automated testing workflow.

01:31:30.000 --> 01:31:38.000
So, um, oftentimes, fabrication of a large number of devices is one thing, and one challenge has been overcome.

01:31:38.000 --> 01:31:42.000
an operation becomes still a bit of a labor intensive.

01:31:42.000 --> 01:31:49.000
So, main reason the operation is a little bit labor intensive, even though all of our operation is pipette-based.

01:31:49.000 --> 01:31:55.000
These are individual devices, so we basically made them into an already format so that, uh, next one.

01:31:55.000 --> 01:31:59.000
So that we can use a multi-channel pipeline or a robotic liquid handling system.

01:31:59.000 --> 01:32:06.000
So we use a low-cost, open-shorn robotic handling system and made our device comparable here.

01:32:06.000 --> 01:32:13.000
And here, basically, about 180 MPS devices can fit in into a single, single run.

01:32:13.000 --> 01:32:18.000
We have, and using this one, next slide, using this one, we were able to basically load.

01:32:18.000 --> 01:32:23.000
or cells into all of these 180 devices with minimum error.

01:32:23.000 --> 01:32:28.000
And then we'll also be able to use media loading, media exchange, as well as.

01:32:28.000 --> 01:32:38.000
eflorn sampling of this operation. So that was a big improvement for us because the big challenge of our operation is the cell loading process.

01:32:38.000 --> 01:32:43.000
And then the every 48-hour, or 48 to 72 hour media exchange process.

01:32:43.000 --> 01:32:49.000
And then the 24-hour media sampling, effluent sampling they're conducting.

01:32:49.000 --> 01:32:54.000
So that we can do a downstream inflammatory cytokine analysis.

01:32:54.000 --> 01:33:06.000
So this really helped us in terms of the operation. And finally, we tested a variety of different polymer to polymer, and then transitioned into an injection molding process.

01:33:06.000 --> 01:33:14.000
of this device so that we can have the fabrication process even much more easier.

01:33:14.000 --> 01:33:28.000
Next. So now, um… Uh, I'm with this device, uh, as I previously mentioned, we have this fetal membrane device, and we have the placental oral chip device.

01:33:28.000 --> 01:33:33.000
So, we were very much interested in looking into the, uh, hazardous.

01:33:33.000 --> 01:33:45.000
how the environment has substances. impact both interfaces to really look into this one comprehensively. So we did, uh, we used both interfaces and, uh, made a comparison. Next.

01:33:45.000 --> 01:33:58.000
So, um… The… in our case, in addition to the early studies of using ketamine, we were very much interested in the PFAS family chemical.

01:33:58.000 --> 01:34:03.000
Because as this audience knows very much, it's a very sensitive chemical major public health concern.

01:34:03.000 --> 01:34:08.000
And, uh, may contribute to preterm growth space in some of these studies coming out.

01:34:08.000 --> 01:34:22.000
So, uh, next. The, uh, hypothesis here is that MPS models can be used to study environmental toxic scan, and they are potentially harmful effect on both the placental as well as fetal membrane interface.

01:34:22.000 --> 01:34:28.000
So specifically, we use 4 different PFAS family chemicals on both placental and felon membrane interface.

01:34:28.000 --> 01:34:34.000
And we looked into both how the direct exposure as well as indirect exposure.

01:34:34.000 --> 01:34:43.000
Uh, can affect the potential. potential pregnancy risk. Next.

01:34:43.000 --> 01:34:55.000
So, uh, in terms of the first thing we do is we tested this PFAS family chemical to make sure that, uh, device surface is not really absorbing, so we tested this one on both.

01:34:55.000 --> 01:35:04.000
The phyto-motonin interface device, as well as the placenta device, looked into absorption. Next slide, we quantify this one by a LCMS.

01:35:04.000 --> 01:35:09.000
Basically, the quick 48-hour study confirmed that there's no chemicals.

01:35:09.000 --> 01:35:25.000
Next one, um, we looked into… next… We looked into, then, direct exposure in the 2D to do a dose range finding. So this is typically how we use a CD for well plate to do a dose range finding.

01:35:25.000 --> 01:35:35.000
Uh, accessibility after 48 hours, next one. Uh, we'll use a cell title, so here you see the fourth one, the seizure, the maternal.

01:35:35.000 --> 01:35:41.000
cell, as well as 3 different fetal cell, and how they respond to the exposure in terms of viability.

01:35:41.000 --> 01:35:53.000
Next slide shows the, uh, next step shows how the placenta cells respond. So you can see that they are responding differently with placenta cells a little bit more resistant to all of the PFAS chemical.

01:35:53.000 --> 01:36:03.000
Next one, then, uh, we looked into, uh, actual device, and, uh, based on the previous dose range finding, we applied the.

01:36:03.000 --> 01:36:08.000
chemical into the seizure chamber, and then in the case of.

01:36:08.000 --> 01:36:12.000
in the case of a placenta, we apply this one to an STV chamber.

01:36:12.000 --> 01:36:18.000
We looked into relying on gravity-driven flow, and then we looked into the response.

01:36:18.000 --> 01:36:26.000
So, if you look at the next one. Uh, what you're seeing here is, um, an incubator for 48 hours.

01:36:26.000 --> 01:36:35.000
We can look into endpoint assay, LCMS, LDH assay, and then cytokine analysis. So, next slide will show the actual result.

01:36:35.000 --> 01:36:43.000
In the case of PFAS on a fetomotin interface, you'll see how the different, forcible propagation occur.

01:36:43.000 --> 01:36:47.000
Next one. And so the result is that.

01:36:47.000 --> 01:36:56.000
PFAS propagate across the device, about 10% by the time it reaches the final, uh, fetal chamber. Next.

01:36:56.000 --> 01:37:06.000
Um, and then, uh, we also looked at the placenta, uh, how the PFAS propagate. Pfas has a bit more of a stronger barrier, so they are retaining PFAS a little bit more.

01:37:06.000 --> 01:37:20.000
Next slide. Uh, next slide will be a viability assessment, so… If you look at the viability, we… this is what you're seeing in comparison to next slide, uh, you can see how placental.

01:37:20.000 --> 01:37:26.000
Uh, placental cells respond. Next.

01:37:26.000 --> 01:37:39.000
So, um, this shows how the viability changes, and if you just go straight to the, uh… entirety of the 27, page 27.

01:37:39.000 --> 01:37:47.000
Yeah, just keep going. So here you are looking at the cytokine analysis of the phenylumetone interface. The LPS was a positive control.

01:37:47.000 --> 01:37:55.000
And depending on the different PFAS chemical that you're seeing a variety of different responses, so next one.

01:37:55.000 --> 01:38:02.000
You look into how different cytokines respond to, in this case, PFDA had the most, uh, induced the most significant fetal inflammation.

01:38:02.000 --> 01:38:06.000
response, especially in the AC, compared with other PFAS.

01:38:06.000 --> 01:38:15.000
Chemical, next one. Now, when we apply this one to the placental interface, you'll see a different response.

01:38:15.000 --> 01:38:24.000
Next one, uh, here, um, so what you're seeing here is that these two interfaces respond, uh, quite differently.

01:38:24.000 --> 01:38:34.000
So, in summary, if you just can continue with the slideshow here, the fetal membrane, direct exposure on the fetal AC showed cytokine responses.

01:38:34.000 --> 01:38:42.000
more reactive to PFAS and a short micellular inflammatory and cytokine cytotoxic response.

01:38:42.000 --> 01:38:49.000
In the case of placenta, drug exposure where trophoblast cells and Huvex cells were more resistant.

01:38:49.000 --> 01:38:55.000
Um… and then a robust barrier to PFAS, where we saw limited propagation.

01:38:55.000 --> 01:39:02.000
And then, uh, finally, uh, truthful is resistance to cell death and inflammation, uh, etc.

01:39:02.000 --> 01:39:07.000
So if you look at the quite summary, cellular and physiological impact.

01:39:07.000 --> 01:39:11.000
So if you look at the summary of these two differences.

01:39:11.000 --> 01:39:16.000
you'll see how the fetal membrane and the placental respond very differently.

01:39:16.000 --> 01:39:22.000
And that really shows the importance of looking into both the fetal membrane as well as the placenta.

01:39:22.000 --> 01:39:31.000
Um, next one. For that, um, so I'll just skip the summary here.

01:39:31.000 --> 01:39:37.000
So, here, I would like to kind of maybe take a last minute to look at what the future direction is.

01:39:37.000 --> 01:39:45.000
So, we have demonstrated that improving ethere is quite important to be able to do this kind of a study.

01:39:45.000 --> 01:39:52.000
Uh, so our high-through automated NEMS model, uh, to have a practical routine utility.

01:39:52.000 --> 01:39:59.000
in a potential hazard of environmental chemical. really having a hierarchy with automated operation is critical.

01:39:59.000 --> 01:40:06.000
And that's really both an ongoing and future incentive theme, not just for our project street, but in many other.

01:40:06.000 --> 01:40:13.000
projects. The second one is… That enables testing broad ranges of PFAS chemical.

01:40:13.000 --> 01:40:18.000
I'm referring to tens to hundreds of different PFAS chemicals.

01:40:18.000 --> 01:40:25.000
Uh, we are ongoing effort in testing both individual chemical and a mixture, and how their response are different.

01:40:25.000 --> 01:40:37.000
That's another key Texas A&M Superfund Center theme. The next one is real-world testing, real-world sample from disaster on other… sorry, can you go back? Another key temperature theme.

01:40:37.000 --> 01:40:43.000
And then, uh, we'd like to establish this one. It has been establishing this one as a mechanistic children study preterm birth.

01:40:43.000 --> 01:40:49.000
And finally, we are trying to incorporate population variability into the MPS model by.

01:40:49.000 --> 01:40:54.000
Using cells from different individuals and test their differential impact.

01:40:54.000 --> 01:40:58.000
And that's another feature. There will be a key feature.

01:40:58.000 --> 01:41:02.000
ongoing, somewhat ongoing in future time, we should perform Sanapim.

01:41:02.000 --> 01:41:10.000
So what we're showing here very much aligned very well to our current and our future theme, and how we.

01:41:10.000 --> 01:41:17.000
How, uh, thematically it fits with the rest of the project. And then, uh, with that, I would like to thank.

01:41:17.000 --> 01:41:25.000
the, uh, all of the team members, so this is really in close collaboration with Dr. Menor's lab at UTMB, Dr. Ivan Rusen's lab at A&M.

01:41:25.000 --> 01:41:32.000
Followed by NIH's Superfund Center as well as the NCATS, some of the NCATS clinical trial on Trace and PS.

01:41:32.000 --> 01:41:42.000
device as well as the NICHG. So with that, I would like to happy to answer any questions that you may have.

01:41:42.000 --> 01:41:45.000
Hey, thank you very much, Dr. Hahn. Fascinating presentation.

01:41:45.000 --> 01:41:52.000
So we have a question here in the question bot, um, what is the film that you use… that you put in the 3D printer made of?

01:41:52.000 --> 01:41:58.000
Have you tested your construction arrays for chemicals that might affect assays?

01:41:58.000 --> 01:42:05.000
How do you background chemical levels from your construction equipment compare with the purchase wells?

01:42:05.000 --> 01:42:10.000
And is there batch-to-batch variation related to the film sources?

01:42:10.000 --> 01:42:20.000
Okay, so first of all, I would like to clarify, the actual device itself is either replica molded molded polymer ore.

01:42:20.000 --> 01:42:33.000
The or the injection molded plastic, which is a reservoir, the 3D printed structure is only for the guide structure, so that's really printed polymer is not in direct contact with the cell.

01:42:33.000 --> 01:42:42.000
Uh, we are very much aware of many of the 3D printed material, especially the photopolymer resin has a potential toxicity.

01:42:42.000 --> 01:42:48.000
So just want to assure that there's no direct contact with the cell and a 3D printed structure. That is more of a.

01:42:48.000 --> 01:42:57.000
sort of more of an experimental fixture that eventually will be anyway made into injection moly plastic.

01:42:57.000 --> 01:43:11.000
Thank you. Um, let's see, there's no other questions. I have one. So, for your experiments, you demonstrated that you can integrate the operation into a liquid handling robotic system.

01:43:11.000 --> 01:43:17.000
So how difficult would this transition be for other MPS devices?

01:43:17.000 --> 01:43:25.000
So, first of all, in our case, our MPS device, from the very beginning, has been a pipette operation-based for two reasons.

01:43:25.000 --> 01:43:29.000
In most cases, having to use a fluidic pumping system.

01:43:29.000 --> 01:43:37.000
I think it makes it much more difficult. Second, in our case, these cell types are typically not exposed to any sort of a high shear stress.

01:43:37.000 --> 01:43:43.000
We actually did a comparison between a dynamic flow versus static no flow.

01:43:43.000 --> 01:43:49.000
And we didn't see any effect. Actually, dynamic flow is having a negative effect. So in our case.

01:43:49.000 --> 01:43:56.000
Uh, any, uh… Transitioning from a pipette-based operation into a multi-channel robotic pipetting system, relatively easy.

01:43:56.000 --> 01:44:02.000
And I think many other MPS devices that has a pipette-based operation and an open well structure.

01:44:02.000 --> 01:44:11.000
will be very easily amenable to transition. Having said that, MPS devices that, for a variety of reasons, have to have a.

01:44:11.000 --> 01:44:17.000
Um, a shear stress, relatively high shear stress, such as, like, a blood vessel, etc.

01:44:17.000 --> 01:44:31.000
Those will be a lot more difficult to transition into a liquid-handed robotic system because of the assurance needed. So I would say some are relatively easy to transition, some might be a little bit more challenging to transition.

01:44:31.000 --> 01:44:36.000
Hey, great, thanks for your response, and thanks for the presentation.

01:44:36.000 --> 01:44:54.000
Um, so, um, I want to thank all the speakers for, um, their great presentations today, and the, um… The folks who are joining in on the webinar, we appreciate your attendance, and I want to also thank Molly for.

01:44:54.000 --> 01:45:08.000
making… hosting this event so seamless, so… Um, thanks again, everyone, and I'll turn it back over to Molly to close this out.

01:45:08.000 --> 01:45:13.000
Thank you. So, before we conclude, let's take a look back at the seminar homepage.

01:45:13.000 --> 01:45:19.000
This website will be active from today on, and contains important resources.

01:45:19.000 --> 01:45:24.000
Such as links to download our presentation materials, contact information for our speakers.

01:45:24.000 --> 01:45:35.000
And a link to our feedback form. We ask that you consider filling out the online feedback form. We do look at your comments as we continue to try to improve the content and delivery mechanisms.

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You can also request a confirmation email from the feedback page as a record of your participation in today's events.

01:45:42.000 --> 01:45:55.000
just look under tips, questions, and support. So here are a few ways to learn more about the Superfund research program. The SRP website homepage link will be posted in the chat.

01:45:55.000 --> 01:45:58.000
And I encourage you to check out the various components of their website.

01:45:58.000 --> 01:46:09.000
To learn more about the program and initiatives. I would also like to remind participants of the various ways to stay connected to ensure that you don't miss any webinars.

01:46:09.000 --> 01:46:15.000
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01:46:15.000 --> 01:46:19.000
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01:46:19.000 --> 01:46:25.000
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01:46:25.000 --> 01:46:29.000
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01:46:29.000 --> 01:46:43.000
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01:46:43.000 --> 01:46:51.000
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01:46:51.000 --> 01:46:57.000
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01:46:57.000 --> 01:47:01.000
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01:47:01.000 --> 01:47:04.000
With that, it is time to conclude today's session.

01:47:04.000 --> 01:47:10.000
Thank you so much for your participation, and thank you to our presenters for their time spent preparing.

01:47:10.000 --> 01:47:25.000
And sharing their presentations with us today.
