logging in or signing up Finch Haggrid Download Post to : URL : Related Presentations : Share Add to Flag Embed Email Send to Blogs and Networks Add to Channel Uploaded from authorPOINTLite Insert YouTube videos in PowerPont slides with aS Desktop Copy embed code: (To copy code, click on the text box) Embed: URL: Thumbnail: WordPress Embed Customize Embed The presentation is successfully added In Your Favorites. Views: 62 Category: Entertainment License: All Rights Reserved Like it (0) Dislike it (0) Added: November 15, 2007 This Presentation is Public Favorites: 0 Presentation Description No description available. Comments Posting comment... Premium member Presentation Transcript Physicochemical Determinants of Beryllium Toxicity using in vitro and in vivo Models: Physicochemical Determinants of Beryllium Toxicity using in vitro and in vivo Models Gregory L. Finch, PhD Drug Safety Evaluation Pfizer Global Research & Development Groton, CT June 25/26, 2002 Beryllium Research Symposium, Bethesda MD Acknowledgement: Most of the research presented today was conducted at Inhalation Toxicology Research Institute [LRRI], Albuquerque, NMCBD: An occupational health mystery: CBD: An occupational health mystery Who? current screening reveals many sensitized and diseased pts only “susceptible” individuals appear to get CBD What? granulomatous lesions with pronounced TH lymphocytic component, with pronounced Be-specific reactivity a debilitating lung disease When? a widely varying latency period following Be exposure; preceded by sensitization Where? mostly occupational following exposure to various Be forms no clear dose-response relationship has been defined Why? an MHC-II restricted response component of genetic susceptibility importance of role of Be physicochemical formSlide3: Model of Be Interaction with Immune System From Newman, 1993Selected observations in role of physicochemical form in CBD: Selected observations in role of physicochemical form in CBD There are a wide variety of physicochemical forms encountered Natural occuring mineral Various “soluble”/”insoluble” forms in processing Mostly insoluble forms delivered to end users Early experience: More soluble forms generally lead to acute Be disease More insoluble forms generally lead to CBD No exposure-dose-response apparent Exposure-response relationships are now being revealed CBD more likely following exposure to relatively insoluble forms apparent excess risk for certain occupations/processesHow can in vitro/in vivo models help?: How can in vitro/in vivo models help? Understanding exposure-dose-response relationships role of physicochemical form acute, episodic, or chronic exposures Linkage to health effects Understanding pathogenesis of response detailed characterization manipulated and/or knock-in/out models Seeking therapeutic intervention Slide6: Lovelace database on the properties and health effects of beryllium aerosolsSlide7: Lovelace database on the properties and health effects of beryllium aerosolsPhysicochemical properties and in vitro characteristics: Physicochemical properties and in vitro characteristics Laboratory-produced preparations BeO: produced with 7Be radiolabel and fired at 500 or 1000oC Be metal: size-fractionated using an aerosol cyclone “Field” preparations Sawing/milling of alloys Laser vaporization of Be metalSlide9: Be Metal Ni-Be Alloy Cu-Be Alloy Softer alloys yielded relatively more fine particles with identical machining processesSlide10: Beryllium Metal Particles Separated by an Aerosol Cyclone Similarities: particle morphology Differences: physical and aerodynamic size; specific surface areaSlide11: Be Metal Particles Have an Oxide Surface Layer Initial dissolution behavior might be similar for Be and BeOSlide12: Solubility in an acidic environment Low fired BeO is more soluble than high fired or metal in an acidic environmentSlide13: Solubility in a simulated lung extracellular fluid BeO is more soluble than Be in simulated lung fluidSlide14: Toxicity to Canine Alveolar Macrophages Toxicity increases with solubility of the Be materialSlide15: In Vitro Toxicity based on: Mass Surface Area Normalization by “surface area dose” resulted in comparable toxicity Large animal models of Be biokinetics and Be-induced toxicity – Studies in Dogs: Large animal models of Be biokinetics and Be-induced toxicity – Studies in Dogs Respirable preparations of 7BeO fired at either 500o or 1000oC were used Dogs were exposed once by inhalation to achieve either low [17 g/kg] or high [50 g/kg] initial lung burdens [ILBs] Dogs were sacrificed up through 365 days post-exposure Biokinetic evaluation Lung histopathology A companion group was evaluated through 730 days post-exposure Period lung lavage for cytology and lymphocyte simulation Dogs were re-exposed at 2-yr then followed for an additional 210 daysSlide17: BeO Clearance/Translocation in Dogs Lower-fired BeO cleared more rapidly from lung, and persisted at higher levels in extrapulmonary compartments LUNGSLung lesion in BeO-exposed dogs: Lung lesion in BeO-exposed dogsInterstitial granuloma in BeO-exposed dogs: Interstitial granuloma in BeO-exposed dogsRelative severity of pulmonary lesions in BeO-exposed dogs: Relative severity of pulmonary lesions in BeO-exposed dogsSlide21: Influence of BeO Temperature History on the Influx of NeutrophilsLymphocyte numbers and SIs in Dogs : Lymphocyte numbers and SIs in Dogs Lymphocyte SIs following re-exposure to BeOGrouped by first exposure to high or low ILBs of 500 or 1000oBeO: Lymphocyte SIs following re-exposure to BeO Grouped by first exposure to high or low ILBs of 500 or 1000oBeOSummary of results in dogs: Summary of results in dogs Compared to high fired BeO, low-fired BeO: cleared from lungs more rapidly produced more marked inflammatory response Increased numbers of lymphocytes Increased lymphocyte stimulation indices Responses peaked several months after exposure Previous exposure history did not influence responses to a 2nd exposure to low-fired BeO, and the effects were not cumulative Comparative toxicity of Be metal vs. BeO in monkeys: Comparative toxicity of Be metal vs. BeO in monkeys Study used low-fired BeO [500oC] and size fractionated Be metal Animals were exposed by bronchoscopic, intrabronchiolar instillation Regimen 1: Graded doses of BeO [saline, 2.5, 12.5, 37.5 g] or Be metal [saline, 1, 50, 150 g] into different lung lobes Doses based on estimated dissolution over 80 dpe Histological evaluation of granulomas guided dose selection for regimen 2 Regimen 2: Single doses of 12.5 g BeO or 50 g Be metal Lavages through 120 dpe and sacrifice at 180 dpe Be-induced lesions in monkey: Be-induced lesions in monkeyBe-induced lesion in monkey: Be-induced lesion in monkeyLymphocytes recovered by lavage: Lymphocytes recovered by lavageLymphocyte proliferation: Lymphocyte proliferationLarge animal studies - summary: Large animal studies - summary Clear differences between BeO [and temperature history] and Be metal demonstrated Biologically: Granulomatous lesions were produced Lymphocytes were increased in number Increased lymphocyte proliferation demonstrated However: Biological responses were not progressive Additional efforts were devoted to murine studies using Be metalSummary of importance of physicochemical form: Summary of importance of physicochemical form It is important for “relatively insoluble” particles The amount of surface presented appears to control dissolution and toxicity Form and preparation influences disposition, biokinetics, and in vivo toxicity Exposure-dose-response need not be rejected Just need to look in the right place Compare “equivalent” exposures Account for host factors, genetic susceptibility Conclusion – a hypothesis: Conclusion – a hypothesis A hypothesis: there is a critical balance in lung between solubility and retained or newly deposited dose Solubility/stimulus: needed to release Be++ to produce antigenic stimulus and induction of sensitization Retention/re-challenge: needed to provide long term challenge depot of Be++ once sensitization is achieved Both form/solubility and chronicity of exposure undoubtably work in concert – with host factors - to drive CBD Acknowledgements: Acknowledgements LRRI Principal Investigators: Greg Finch Mark Hoover Pat Haley LRRI Scientists Ed Barr Bill Bechtold Dave Bice Fletcher Hahn Charles Hobbs Tom March Bruce Muggenburg Kris Nikula Bill Griffith Janet Benson Steve Belinsky Technical Support Staff: Lee Blair Dee Esparza Anna Holmes Applied Toxicology Group Exposure Operations Group Animal Care Unit Necropsy/Histology Lab Lung Cancer Program Collaborations: Bill Carlton, DVM, Purdue Alan Rebar, DVM, Purdue Funding from the US Department of Energy You do not have the permission to view this presentation. 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Finch Haggrid Download Post to : URL : Related Presentations : Share Add to Flag Embed Email Send to Blogs and Networks Add to Channel Uploaded from authorPOINTLite Insert YouTube videos in PowerPont slides with aS Desktop Copy embed code: (To copy code, click on the text box) Embed: URL: Thumbnail: WordPress Embed Customize Embed The presentation is successfully added In Your Favorites. Views: 62 Category: Entertainment License: All Rights Reserved Like it (0) Dislike it (0) Added: November 15, 2007 This Presentation is Public Favorites: 0 Presentation Description No description available. Comments Posting comment... Premium member Presentation Transcript Physicochemical Determinants of Beryllium Toxicity using in vitro and in vivo Models: Physicochemical Determinants of Beryllium Toxicity using in vitro and in vivo Models Gregory L. Finch, PhD Drug Safety Evaluation Pfizer Global Research & Development Groton, CT June 25/26, 2002 Beryllium Research Symposium, Bethesda MD Acknowledgement: Most of the research presented today was conducted at Inhalation Toxicology Research Institute [LRRI], Albuquerque, NMCBD: An occupational health mystery: CBD: An occupational health mystery Who? current screening reveals many sensitized and diseased pts only “susceptible” individuals appear to get CBD What? granulomatous lesions with pronounced TH lymphocytic component, with pronounced Be-specific reactivity a debilitating lung disease When? a widely varying latency period following Be exposure; preceded by sensitization Where? mostly occupational following exposure to various Be forms no clear dose-response relationship has been defined Why? an MHC-II restricted response component of genetic susceptibility importance of role of Be physicochemical formSlide3: Model of Be Interaction with Immune System From Newman, 1993Selected observations in role of physicochemical form in CBD: Selected observations in role of physicochemical form in CBD There are a wide variety of physicochemical forms encountered Natural occuring mineral Various “soluble”/”insoluble” forms in processing Mostly insoluble forms delivered to end users Early experience: More soluble forms generally lead to acute Be disease More insoluble forms generally lead to CBD No exposure-dose-response apparent Exposure-response relationships are now being revealed CBD more likely following exposure to relatively insoluble forms apparent excess risk for certain occupations/processesHow can in vitro/in vivo models help?: How can in vitro/in vivo models help? Understanding exposure-dose-response relationships role of physicochemical form acute, episodic, or chronic exposures Linkage to health effects Understanding pathogenesis of response detailed characterization manipulated and/or knock-in/out models Seeking therapeutic intervention Slide6: Lovelace database on the properties and health effects of beryllium aerosolsSlide7: Lovelace database on the properties and health effects of beryllium aerosolsPhysicochemical properties and in vitro characteristics: Physicochemical properties and in vitro characteristics Laboratory-produced preparations BeO: produced with 7Be radiolabel and fired at 500 or 1000oC Be metal: size-fractionated using an aerosol cyclone “Field” preparations Sawing/milling of alloys Laser vaporization of Be metalSlide9: Be Metal Ni-Be Alloy Cu-Be Alloy Softer alloys yielded relatively more fine particles with identical machining processesSlide10: Beryllium Metal Particles Separated by an Aerosol Cyclone Similarities: particle morphology Differences: physical and aerodynamic size; specific surface areaSlide11: Be Metal Particles Have an Oxide Surface Layer Initial dissolution behavior might be similar for Be and BeOSlide12: Solubility in an acidic environment Low fired BeO is more soluble than high fired or metal in an acidic environmentSlide13: Solubility in a simulated lung extracellular fluid BeO is more soluble than Be in simulated lung fluidSlide14: Toxicity to Canine Alveolar Macrophages Toxicity increases with solubility of the Be materialSlide15: In Vitro Toxicity based on: Mass Surface Area Normalization by “surface area dose” resulted in comparable toxicity Large animal models of Be biokinetics and Be-induced toxicity – Studies in Dogs: Large animal models of Be biokinetics and Be-induced toxicity – Studies in Dogs Respirable preparations of 7BeO fired at either 500o or 1000oC were used Dogs were exposed once by inhalation to achieve either low [17 g/kg] or high [50 g/kg] initial lung burdens [ILBs] Dogs were sacrificed up through 365 days post-exposure Biokinetic evaluation Lung histopathology A companion group was evaluated through 730 days post-exposure Period lung lavage for cytology and lymphocyte simulation Dogs were re-exposed at 2-yr then followed for an additional 210 daysSlide17: BeO Clearance/Translocation in Dogs Lower-fired BeO cleared more rapidly from lung, and persisted at higher levels in extrapulmonary compartments LUNGSLung lesion in BeO-exposed dogs: Lung lesion in BeO-exposed dogsInterstitial granuloma in BeO-exposed dogs: Interstitial granuloma in BeO-exposed dogsRelative severity of pulmonary lesions in BeO-exposed dogs: Relative severity of pulmonary lesions in BeO-exposed dogsSlide21: Influence of BeO Temperature History on the Influx of NeutrophilsLymphocyte numbers and SIs in Dogs : Lymphocyte numbers and SIs in Dogs Lymphocyte SIs following re-exposure to BeOGrouped by first exposure to high or low ILBs of 500 or 1000oBeO: Lymphocyte SIs following re-exposure to BeO Grouped by first exposure to high or low ILBs of 500 or 1000oBeOSummary of results in dogs: Summary of results in dogs Compared to high fired BeO, low-fired BeO: cleared from lungs more rapidly produced more marked inflammatory response Increased numbers of lymphocytes Increased lymphocyte stimulation indices Responses peaked several months after exposure Previous exposure history did not influence responses to a 2nd exposure to low-fired BeO, and the effects were not cumulative Comparative toxicity of Be metal vs. BeO in monkeys: Comparative toxicity of Be metal vs. BeO in monkeys Study used low-fired BeO [500oC] and size fractionated Be metal Animals were exposed by bronchoscopic, intrabronchiolar instillation Regimen 1: Graded doses of BeO [saline, 2.5, 12.5, 37.5 g] or Be metal [saline, 1, 50, 150 g] into different lung lobes Doses based on estimated dissolution over 80 dpe Histological evaluation of granulomas guided dose selection for regimen 2 Regimen 2: Single doses of 12.5 g BeO or 50 g Be metal Lavages through 120 dpe and sacrifice at 180 dpe Be-induced lesions in monkey: Be-induced lesions in monkeyBe-induced lesion in monkey: Be-induced lesion in monkeyLymphocytes recovered by lavage: Lymphocytes recovered by lavageLymphocyte proliferation: Lymphocyte proliferationLarge animal studies - summary: Large animal studies - summary Clear differences between BeO [and temperature history] and Be metal demonstrated Biologically: Granulomatous lesions were produced Lymphocytes were increased in number Increased lymphocyte proliferation demonstrated However: Biological responses were not progressive Additional efforts were devoted to murine studies using Be metalSummary of importance of physicochemical form: Summary of importance of physicochemical form It is important for “relatively insoluble” particles The amount of surface presented appears to control dissolution and toxicity Form and preparation influences disposition, biokinetics, and in vivo toxicity Exposure-dose-response need not be rejected Just need to look in the right place Compare “equivalent” exposures Account for host factors, genetic susceptibility Conclusion – a hypothesis: Conclusion – a hypothesis A hypothesis: there is a critical balance in lung between solubility and retained or newly deposited dose Solubility/stimulus: needed to release Be++ to produce antigenic stimulus and induction of sensitization Retention/re-challenge: needed to provide long term challenge depot of Be++ once sensitization is achieved Both form/solubility and chronicity of exposure undoubtably work in concert – with host factors - to drive CBD Acknowledgements: Acknowledgements LRRI Principal Investigators: Greg Finch Mark Hoover Pat Haley LRRI Scientists Ed Barr Bill Bechtold Dave Bice Fletcher Hahn Charles Hobbs Tom March Bruce Muggenburg Kris Nikula Bill Griffith Janet Benson Steve Belinsky Technical Support Staff: Lee Blair Dee Esparza Anna Holmes Applied Toxicology Group Exposure Operations Group Animal Care Unit Necropsy/Histology Lab Lung Cancer Program Collaborations: Bill Carlton, DVM, Purdue Alan Rebar, DVM, Purdue Funding from the US Department of Energy