Gene/Protein Disease Symptom Drug Enzyme Compound
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Query: UNIPROT:P02794 (ferritin)
17,525 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

Bleomycin-reactive iron was detected in the sera of six out of nine adults undergoing intensive chemotherapy for acute non-lymphocytic leukemia. In these individuals the corresponding transferrin saturation ranged from 96% to 113% and the serum ferritin from 775 to 9975 micrograms/l. Nontransferrin-bound iron has been postulated to be a factor in organ toxicity in iron overload conditions such as beta thalassemia and hereditary hemochromatosis by facilitating the production of tissue-damaging free radicals. We propose that bleomycin-reactive iron should be considered as a possible factor in organ dysfunction seen with intensive cancer chemotherapy.
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PMID:Bleomycin-reactive iron in patients with acute non-lymphocytic leukemia. 137 50

Plasma from patients with iron overload resulting from idiopathic hemochromatosis contains nontransferrin-bound iron, measurable by the bleomycin, assay. During venesection therapy, the concentration of bleomycin iron declines in a way highly correlated with plasma ferritin concentrations. Even when patients had been venesected to give very low total plasma iron concentrations and high transferrin iron-binding capacity, bleomycin-detectable iron was still present at low concentrations. Bleomycin-detectable iron can stimulate damaging free radical reactions, and its persistence in plasma even after prolonged venesection might contribute to the tissue damage that results from iron overload.
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PMID:Nontransferrin-bound iron in plasma from hemochromatosis patients: effect of phlebotomy therapy. 245 83

Foamy alveolar macrophages (FAM) are observed in lungs injured by Bleomycin (BLM), but their relation to pulmonary fibrosis is not clearly understood. We purified FAM from BLM-instilled rat lungs by density gradient centrifugation on Percoll, and studied the effect of FAM on pulmonary fibrosis. The cells lavaged from the rat lungs 14 days after the administration of BLM (B) or saline (S), were applied on Percoll. After centrifugation, the cells layered on each interface were collected and named as SI, SII, SIII, and BI, BII, BIII in order of gravity. The BI layer included 8.5% of unfractionated cells (U). These BI cells were viable (88%), significantly larger than the others, nonspecific esterase positive cells, and included much ferritin and lysozyme, and were morphologically identified as alveolar macrophages (AM). Therefore, we called the BI cells FAM. We estimated the capacity of FAM (2.5 X 10(5] to synthesize DNA (3H-thymidine uptake) and RNA (3H-uridine uptake), and the activities of silica-stimulated FAM to cause proliferation of mouse thymocytes (IL-1 activity) and rat lung fibroblasts (FP activity), and to produce PGE2. FAM has a lower mitogenic activity but did not have been protein synthetic activity as compared with the others. Silica-stimulated FAM released less IL-1 than BII or BIII, and induced less fibroblast growth than BII, but induced as much as BIII, possibly because of the increased capacity of BIII cells to produce PGE2, which is known to inhibit fibroblast growth. In this way, FAM were considered to be "already activated" rather than "highly activated" cells, but the presence of FAM suggested that smaller or denser AM might receive bleomycin stimulation and release fibrogenic mediators (IL-1 or MDGF) into the alveolar spaces during FAM formation, and that AM might participate in the fibrogenic responses.
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PMID:[The effect of foamy alveolar macrophages presented in bleomycin-injured rat lungs in pulmonary fibrosis]. 247 35

Establishment of water quality criteria (WQC), intended to protect aquatic life, continues to rely principally on water hardness (i.e. Ca(2+)) for lead (Pb) despite growing evidence that other chemical parameters also strongly influence toxicity. To more clearly define the water chemistry parameters mediating Pb toxicity, we evaluated the effects of hardness as CaSO(4) and dissolved organic carbon (DOC) as humic acid during chronic (150 days) exposures to the fathead minnow. Measured Pb concentrations ranged from 157+/-5 nM (33+/-1 microg/L) Pb in base water to 177+/-7 (37+/-1 microg/L) and 187+/-7 nM (39+/-1 microg/L) Pb in CaSO(4)- or HA-supplemented water, respectively. Fish were collected at 2, 4, 10, 30, 63, 90 and 150 days of exposure. Traditional toxicological endpoints were examined alongside gene transcription analyses to help clarify the underlying mechanisms of Pb toxicity and to identify candidate molecular markers that might ultimately serve as robust indicators of exposure and effect. Addition of CaSO(4) did not prevent whole body Pb accumulation whereas DOC afforded strong protection (about half the amount accumulated by fish in base water) suggesting that current, hardness-based WQC are likely inaccurate for predicting chronic Pb effects in aquatic systems. Custom-made microarrays were co-hybridized with base water samples+/-Pb up to the 30 days time point. Quantitative PCR was employed to verify gene transcription responses and to extend analysis to the CaSO(4) and HA treatments and the 150 days time point. Identification of four genes by microarray analysis revealed clear Pb-induced responses over time: glucose-6-phosphate dehydrogenase, glutathione-S-transferase, ferritin and beta-globin. Results obtained by qPCR were in strong agreement with microarray data by regression analysis (r(2)=0.82, slope=1.28). The associated pathways implicated herein for these genes provide further evidence supporting roles for anemia and neurological disorders in chronic Pb toxicity. Effects of water chemistry on Pb accumulation and gene transcription responses were in close parallel, though alterations in ionoregulatory and morphological endpoints were not observed. Whereas DOC was protective against Pb accumulation and mRNA expression changes, Ca(2+) was not. Additionally, several hypothesis-driven genes (ECaC, DMT-1, and ALA-D) were examined by qPCR but revealed either no change or small Pb-induced responses lacking any clear influence attributable to water chemistry. These findings should help pave the way toward development of a new chronic Pb BLM and a Pb-responsive gene transcript profile for fathead minnows, both of which would greatly aid future environmental monitoring and regulatory strategies for Pb.
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PMID:Toxicogenomics of water chemistry influence on chronic lead exposure to the fathead minnow (Pimephales promelas). 1834 99