13 research outputs found
Table1_Prognosis-related genes participate in immunotherapy of renal clear cell carcinoma possibly by targeting dendritic cells.XLSX
Tumor immunotherapy has become one of the most promising approaches to tumor treatment. This study aimed to screen genes involved in the response of clear cell renal cell carcinoma (ccRCC) to immunotherapy and analyze their function. Based on the Gene Expression Omnibus and The Cancer Genome Atlas datasets, we screened out nine differentially expressed genes (TYROBP, APOC1, CSTA, LY96, LAPTM5, CD300A, ALOX5, C1QA, and C1QB) associated with clinical traits and prognosis. A risk signature constructed by these nine genes could predict the survival probability for patients at 1 year, 3 years, and 5 years. The immune checkpoint blockade response rate in the high-risk group was significantly higher than in the low-risk group (49.25% vs. 24.72%, p ≤ 0.001). The nine prognosis-related genes were negatively correlated with activated dendritic cells in the low-risk group but not in the high-risk group. qRT-PCR, immunohistochemistry, and immunofluorescence showed that the nine prognosis-related genes were associated with dendritic cell activity and the PD-1 positive staining rate. In conclusion, the nine prognosis-related genes have a high prognostic value. The patients in the high-risk group were more likely to benefit from immunotherapy, and the mechanism might be related to the release of dendritic cell-mediated immunosuppression.</p
Table5_Prognosis-related genes participate in immunotherapy of renal clear cell carcinoma possibly by targeting dendritic cells.XLSX
Tumor immunotherapy has become one of the most promising approaches to tumor treatment. This study aimed to screen genes involved in the response of clear cell renal cell carcinoma (ccRCC) to immunotherapy and analyze their function. Based on the Gene Expression Omnibus and The Cancer Genome Atlas datasets, we screened out nine differentially expressed genes (TYROBP, APOC1, CSTA, LY96, LAPTM5, CD300A, ALOX5, C1QA, and C1QB) associated with clinical traits and prognosis. A risk signature constructed by these nine genes could predict the survival probability for patients at 1 year, 3 years, and 5 years. The immune checkpoint blockade response rate in the high-risk group was significantly higher than in the low-risk group (49.25% vs. 24.72%, p ≤ 0.001). The nine prognosis-related genes were negatively correlated with activated dendritic cells in the low-risk group but not in the high-risk group. qRT-PCR, immunohistochemistry, and immunofluorescence showed that the nine prognosis-related genes were associated with dendritic cell activity and the PD-1 positive staining rate. In conclusion, the nine prognosis-related genes have a high prognostic value. The patients in the high-risk group were more likely to benefit from immunotherapy, and the mechanism might be related to the release of dendritic cell-mediated immunosuppression.</p
Key Role of Persistent Free Radicals in Hydrogen Peroxide Activation by Biochar: Implications to Organic Contaminant Degradation
We
investigated the activation of hydrogen peroxide (H<sub>2</sub>O<sub>2</sub>) by biochars (produced from pine needles, wheat, and
maize straw) for 2-chlorobiphenyl (2-CB) degradation in the present
study. It was found that H<sub>2</sub>O<sub>2</sub> can be effectively
activated by biochar, which produces hydroxyl radical (<sup>•</sup>OH) to degrade 2-CB. Furthermore, the activation mechanism was elucidated
by electron paramagnetic resonance (EPR) and salicylic acid (SA) trapping
techniques. The results showed that biochar contains persistent free
radicals (PFRs), typically ∼10<sup>18</sup> unpaired spins/gram.
Higher trapped [<sup>•</sup>OH] concentrations were observed
with larger decreases in PFRs concentration, when H<sub>2</sub>O<sub>2</sub> was added to biochar, indicating that PFRs were the main
contributor to the formation of <sup>•</sup>OH. This hypothesis
was supported by the linear correlations between PFRs concentration
and trapped [<sup>•</sup>OH], as well as <i>k</i><sub>obs</sub> of 2-CB degradation. The correlation coefficients
(<i>R</i><sup>2</sup>) were 0.723 and 0.668 for PFRs concentration
vs trapped [<sup>•</sup>OH], and PFRs concentration vs <i>k</i><sub>obs</sub>, respectively, when all biochars pyrolyzed
at different temperatures were included. For the same biochar washed
by different organic solvents (methanol, hexane, dichloromethane,
and toluene), the correlation coefficients markedly increased to 0.818–0.907.
Single-electron transfer from PFRs to H<sub>2</sub>O<sub>2</sub> was
a possible mechanism for H<sub>2</sub>O<sub>2</sub> activation by
biochars, which was supported by free radical quenching studies. The
findings of this study provide a new pathway for biochar implication
and insight into the mechanism of H<sub>2</sub>O<sub>2</sub> activation
by carbonaceous materials (e.g., activated carbon and graphite)
A Mechanistic Understanding of Hydrogen Peroxide Decomposition by Vanadium Minerals for Diethyl Phthalate Degradation
The
interaction of naturally occurring minerals with H<sub>2</sub>O<sub>2</sub> affects the remediation efficiency of polluted sites
in in situ chemical oxidation (ISCO) treatments. However, interactions
between vanadiumÂ(V) minerals and H<sub>2</sub>O<sub>2</sub> have rarely
been explored. In this study, H<sub>2</sub>O<sub>2</sub> decomposition
by various vanadium-containing minerals including VÂ(III), VÂ(IV), and
VÂ(V) oxides was examined, and the mechanism of hydroxyl radical (<sup>•</sup>OH) generation for contaminant degradation was studied.
Vanadium minerals were found to catalyze H<sub>2</sub>O<sub>2</sub> decomposition efficiently to produce <sup>•</sup>OH for diethyl
phthalate (DEP) degradation in both aqueous solutions with a wide
pH range and in soil slurry. Electron paramagnetic resonance (EPR),
X-ray photoelectron spectroscopy (XPS), X-ray diffraction (XRD) analyses,
and free radical quenching studies suggested that <sup>•</sup>OH was produced via single electron transfer from VÂ(III)/VÂ(IV) to
H<sub>2</sub>O<sub>2</sub> followed a Fenton-like pathway on the surface
of V<sub>2</sub>O<sub>3</sub> and VO<sub>2</sub> particles, whereas
the oxygen vacancy (OV) was mainly responsible for <sup>•</sup>OH formation on the surface of V<sub>2</sub>O<sub>5</sub> particles.
This study provides new insight into the mechanism of interactions
between vanadium minerals and H<sub>2</sub>O<sub>2</sub> during H<sub>2</sub>O<sub>2</sub>-based ISCO
Reductive Hexachloroethane Degradation by S<sub>2</sub>O<sub>8</sub><sup>•–</sup> with Thermal Activation of Persulfate under Anaerobic Conditions
Despite
that persulfate radical (S<sub>2</sub>O<sub>8</sub><sup>•–</sup>) is an important radical species formed from
the persulfate (PS) activation process, its reactivity toward contaminant
degradation has rarely been explored. In this study, we found that
S<sub>2</sub>O<sub>8</sub><sup>•–</sup> efficiently
degrades the contaminant hexachloroethane (HCA) under anaerobic conditions,
whereas HCA degradation is negligible in the presence of oxygen. We
observed dechlorination products such as pentachloroethane, tetrachloroethylene,
and Cl<sup>–</sup> during HCA degradation, which suggest that
HCA degradation is mainly a reductive process under anaerobic conditions.
Using free radical quenching and electron paramagnetic resonance (EPR)
experiments, we confirmed that S<sub>2</sub>O<sub>8</sub><sup>•–</sup> forms from the reaction between sulfate radical (SO<sub>4</sub><sup>•–</sup>) and S<sub>2</sub>O<sub>8</sub><sup>2–</sup>, which are the dominant reactive species in HCA degradation. Density
functional theory (DFT) calculations were used to elucidate the pathways
of HCA degradation and S<sub>2</sub>O<sub>8</sub><sup>•–</sup> radical decomposition. Further investigation showed that S<sub>2</sub>O<sub>8</sub><sup>•–</sup> can efficiently degrade
HCA and DDTs in soil via reduction during the thermal activation of
PS under anaerobic conditions. The finding of this study provide a
novel strategy for the reductive degradation of contaminant when PS-based
in situ chemical oxidation used in the remediation of soil and groundwater,
particularly those contaminated with highly halogenated compounds
Fate of As(III) and As(V) during Microbial Reduction of Arsenic-Bearing Ferrihydrite Facilitated by Activated Carbon
Microbial
reduction of arsenic (As)-bearing FeÂ(III)-(oxyhydr)Âoxides
is one of the major processes for the release of As in various environmental
settings such as acid mine drainage, groundwater, and flooded paddy
soil. Pyrogenic carbon has recently been reported to facilitate microbial
extracellular reduction of FeÂ(III)-(oxyhydr)Âoxides. The aim of this
study was to investigate the important hot topic regarding the fate
and transformation of As during activated carbon (AC) facilitated
microbial reduction of As-bearing ferrihydrite. Our results show that
the rate and extent of FeÂ(III) reduction in As-bearing ferrihydrite
by <i>Shewanella oneidensis</i> MR-1 were accelerated by
AC. The AC facilitated reduction caused the release of AsÂ(III) into
the solution, whereas it caused the preferential immobilization of
AsÂ(V) on the solid phase. Furthermore, AC accelerated the precipitation
of vivianite and siderite in sequence during microbial reduction processes.
Both of the formed vivianite and siderite had an insignificant capacity
for capturing AsÂ(III); however, AsÂ(V) was selectively immobilized
by vivianite compared to that of siderite. Taken together, our findings
provide crucial insights into understanding the role of AC on the
redox and immobilization of Fe and As in suboxic and anoxic environments
and thus their environmental fate when pyrogenic carbons are employed
for agronomic and environmental applications
Intracellular localization of SP-A2 wild-type and variants.
<p>CHO-K1 Cells were transiently transfected with SP-A2 wild-type, G231V, F198S, Q223K plasmids, 48 h after transfection, the cells were fixed by 4% PFA, the localization of SP-A2 was examined by indirect immunofluorescence assay, and images were collected by confocal microscopy as described in Materials and Methods. Wild-type and Q223K distributed evenly in cellular which colocalized in part with calreticulin (ER marker) (<b>H,T</b>). Most of G231V, F198S mutants colocalized with calreticulin (<b>L,P</b>). Scale bar 10 µm.</p
Expression of SP-A2 wild-type and mutant protein and mRNA in CHO-K1 cells.
<p>(<b>A</b>) SP-A2 schematic. SP-A2 is tagged with V5 epitope at amino acid position 21 follow the signal sequence, four functional domains are indicated, and various mutations are also listed. <b>CRD</b>, carbohydrate recognition domain. (<b>B</b>) CHO-K1 cells were transiently transfected with vector (pcDNA3.0), V5-tagged SP-A2 wild-type, G231V, F198S and Q223K variants full-length cDNA plasmids. Forty-eight hours after transfection, equal amounts of total protein from cell lysate or media were subjected to SDS-PAGE and followed by immunoblot analysis using a monoclonal antibody that recognizes the V5 epitope. (<b>C</b>) Stably expressing vector, V5-tagged SP-A2 wild-type, G231V, F198S and Q223K variants in CHO-K1 cells. 5×10<sup>5</sup> cells/well were seeded and cultured in 6-well plate for 48 h, cell lysate and medium were collected and analyzed by SDS-PAGE and western blotting. (<b>D</b>) CHO-K1 cells were transiently transfected with plasmids pcDNA3.0, V5-tagged SP-A2 wild-type, G231V, F198S and Q223K variants. Forty-eight hours later, total RNA was extracted and RT-PCR was performed using primers specific to SP-A2 and GAPDH gene.</p
Analysis of glycosylation modifications of human SP-A2 in cell lysate and medium.
<p>CHO-K1 Cells were transiently expressed SP-A2 wild-type, G231V, F198S or d (100–133) plasmids for 48 h and the cell lysate (<b>A and C</b>) or medium (<b>B</b>) were treated without or with (+) PNGase F, Endo H, Neuraminidase, O-glycosidase as described in Materials and methods. Digestion products were subjected to SDS-PAGE, transferred to NC membranes, immunoblotted with anti-V5 antibody. <b>a</b>.Mature and sialylated SP-A2 protein. <b>b.</b> Desialylated SP-A2. <b>c.</b> Immature N-glycosylated SP-A2, but not sialylated. <b>d.</b> Deglycosylated SP-A2. Presence and linkage patterns of terminally linked sialic acids on mature secreted SP-A2 from medium were further analyzed by immuoprecipitation and Western blotting, followed by detection with digoxigenin-labeled lectins and anti-digoxigenin-alkaline phosphatase system (<b>D and E</b>). To assess lectin binding efficiency and specificity both positive control glycoproteins (fetuin for <i>α</i>(2,3)-linkage and transferrin for <i>α</i>(2,6)-linkage) and negative control (N-Glycosidase F treated transferrin) were included.</p
SP-A2 G231V, F198S proteins partially degraded through proteasome pathway but not lysosome or autophagy pathway.
<p>(<b>A–D</b>) CHO-K1 Cells were transiently expressed SP-A2 wild-type, G231V, F198S, Q223K plasmids, 24 h later change medium and treated the cell with ALLN (<b>A</b>), MG-132 (<b>B</b>), 3-MA (<b>C</b>), leupeptin (<b>D</b>) for 24 h, then cell lysate and medium were collected, analyzed by SDS-PAGE and western blotting. (<b>E</b>) SP-A2 Neck region (100–133) mutant expression is increased by inhibition of proteasome pathway but not lysosome or autophagy pathway. The amount of each SP-A variant was normalized to its expression in the absence of inhibitors. Data are shown as the mean±S.D. for at least three independent transfection experiments.</p