Oak Ridge Institute for Science and Education Research Participation Program, U.S. Environmental Protection Agency, Research Triangle Park, NC, USA.
Public Health and Integrated Toxicology Division, Center for Public Health and Environmental Assessment, U.S. Environmental Protection Agency, Research Triangle Park, NC, USA.
Inhal Toxicol. 2023 Mar-Apr;35(3-4):59-75. doi: 10.1080/08958378.2022.2100019. Epub 2022 Jul 22.
Inhalation of ozone activates central sympathetic-adrenal-medullary and hypothalamic-pituitary-adrenal stress axes. While airway neural networks are known to communicate noxious stimuli to higher brain centers, it is not known to what extent responses generated from pulmonary airways contribute to neuroendocrine activation.
Unlike inhalational exposures that involve the entire respiratory tract, we employed intratracheal (IT) instillations to expose only pulmonary airways to either soluble metal-rich residual oil fly ash (ROFA) or compressor-generated diesel exhaust particles (C-DEP). Male Wistar-Kyoto rats (12-13 weeks) were IT instilled with either saline, C-DEP or ROFA (5 mg/kg) and necropsied at 4 or 24 hr to assess temporal effects.
IT-instillation of particulate matter (PM) induced hyperglycemia as early as 30-min and glucose intolerance when measured at 2 hr post-exposure. We observed PM- and time-specific effects on markers of pulmonary injury/inflammation (ROFA>C-DEP; 24 hr>4hr) as corroborated by increases in lavage fluid injury markers, neutrophils (ROFA>C-DEP), and lymphocytes (ROFA). Increases in lavage fluid pro-inflammatory cytokines differed between C-DEP and ROFA in that C-DEP caused larger increases in TNF-α whereas ROFA caused larger increases in IL-6. No increases in circulating cytokines occurred. At 4 hr, PM impacts on neuroendocrine activation were observed through depletion of circulating leukocytes, increases in adrenaline (ROFA), and decreases in thyroid-stimulating-hormone, T, prolactin, luteinizing-hormone, and testosterone. C-DEP and ROFA both increased lung expression of genes involved in acute stress and inflammatory processes. Moreover, small increases occurred in hypothalamic , a glucocorticoid-sensitive gene.
Respiratory alterations differed between C-DEP and ROFA, with ROFA inducing greater overall lung injury/inflammation; however, both PM induced a similar degree of neuroendocrine activation. These findings demonstrate neuroendocrine activation after pulmonary-only PM exposure, and suggest the involvement of pituitary- and adrenal-derived hormones.
臭氧吸入会激活中枢交感肾上腺髓质和下丘脑垂体肾上腺应激轴。虽然气道神经网络已知将有害刺激传递到大脑中枢,但尚不清楚从肺部气道产生的反应在多大程度上有助于神经内分泌激活。
与涉及整个呼吸道的吸入暴露不同,我们采用气管内(IT)滴注的方法,仅使肺部气道暴露于富含可溶性金属的残余油飞灰(ROFA)或压缩机产生的柴油排气颗粒(C-DEP)。雄性 Wistar-Kyoto 大鼠(12-13 周)经 IT 滴注生理盐水、C-DEP 或 ROFA(5mg/kg),并在 4 或 24 小时后解剖以评估时间效应。
颗粒物(PM)的 IT 滴注在 30 分钟时引起高血糖,在暴露后 2 小时时引起葡萄糖不耐受。我们观察到 PM 及时间特异性对肺损伤/炎症标志物的影响(ROFA>C-DEP;24 小时>4 小时),这与灌洗液损伤标志物、中性粒细胞(ROFA>C-DEP)和淋巴细胞(ROFA)的增加相吻合。C-DEP 和 ROFA 之间的灌洗液促炎细胞因子增加存在差异,C-DEP 导致 TNF-α增加较大,而 ROFA 导致 IL-6 增加较大。循环细胞因子没有增加。在 4 小时时,通过消耗循环白细胞、增加肾上腺素(ROFA)和降低促甲状腺激素 T、催乳素、黄体生成素和睾酮,观察到 PM 对神经内分泌激活的影响。C-DEP 和 ROFA 均增加了参与急性应激和炎症过程的肺基因表达。此外,下丘脑的基因表达也略有增加,这是一种糖皮质激素敏感基因。
C-DEP 和 ROFA 之间的呼吸变化不同,ROFA 引起更大程度的整体肺损伤/炎症;然而,两种 PM 都引起了类似程度的神经内分泌激活。这些发现表明,在仅肺部 PM 暴露后会发生神经内分泌激活,并提示垂体和肾上腺源性激素的参与。