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At least 19 recordsLinked to original sources

Biologic-biologic and biologic-JAK inhibitor combination therapy in refractory systemic autoinflammatory diseases.

OBJECTIVES: Systemic autoinflammatory diseases (SAIDs) arise from genetic defects in innate immunity, leading to dysregulated activation of inflammatory pathways, including interleukin (IL)-1, IL-6, TNF, and JAK/STAT. Clinical manifestations range from recurrent fever to severe complications such as encephalitis and AA amyloidosis. Management aims to control inflammation using immunosuppressive agents and targeted monotherapies (biologics or JAK inhibitors). Advanced combination therapy (ACT), defined as the use of biologics and/or JAK inhibitors in combination, has emerged as a strategy for refractory disease. METHODS: In this observational retrospective longitudinal cohort study, patients with SAIDs treated with ACT were included. Demographic, clinical, treatment, and safety data were collected. Treatment response was assessed using a composite outcome incorporating corticosteroid dose, C-reactive protein (CRP), and clinical improvement and categorized as non-response, partial response, or complete response. RESULTS: Thirty-eight patients (median age 30 years [range 4-76]) were included. The most common indications for ACT were pyogenic arthritis, pyoderma gangrenosum and acne (PAPA), mevalonate kinase deficiency (MKD), and undifferentiated SAIDs. Most patients had disease-related complications and were dependent on glucocorticoids and/or opioids to control inflammation and pain, respectively. Following multiple ACT trials, complete response was observed in 21 patients (55.3%), partial response in 12 (31.6%), and no response in 5 (13.1%). Overall, 65 ACT regimens were administered, most commonly combining IL-1 and TNF inhibitors. Thirty-nine regimens were discontinued because of lack of efficacy, secondary loss of response, or adverse events. At the final follow-up, 26 patients (68%) remained on ACT, with a median treatment duration of 60 months (range, 11-186). CONCLUSIONS: ACT offers significant clinical benefits for patients with difficult-to-treat SAIDs, though challenges such as secondary loss of efficacy and infection risks remain.

Humans

Evaluation of a rapid readout biological indicator for flash sterilization with three biological indicators and three chemical indicators.

OBJECTIVE: Flash sterilization is most commonly used for emergency sterilization of unwrapped items in a gravity displacement sterilizer for three minutes. Sterilization quality assurance is monitored by biological indicators that require a 24-hour incubation prior to reading. In this study, we compared a new biological indicator that provides results within 60 minutes with three conventional, 24-hour biological indicators for monitoring flash sterilization and three chemical indicators. DESIGN: Conventional biological indicators tested included the conventional Attest 1261, Proof Flash and Assert, while the rapid readout indicator tested was Attest 1291. Attest Rapid Readout detects the presence of a Bacillus stearothermophilus enzyme by reading a fluorescent product that is produced by the enzymatic break-down of a nonfluorescent substrate. Chemical indicators tested included Comply, Incheque, and Thermalog S. Survival at 132 degrees C in a gravity displacement sterilizer was measured by media color change after incubation for 24 hours at 56 degrees C for the three conventional biological indicators, fluorescence at 60 minutes for the Attest Rapid Readout biological indicator, and color change for the chemical indicators. Each exposure time was replicated four times with 10 of each biological and chemical indicator per run. RESULTS: The conventional biological indicators (Attest, Proof Flash, and Assert) had 90%, 48%, and 40% spore survival at two minutes exposure; 23%, 3%, and 0% at three minutes exposure; and 3%, 0%, and 0% at four minutes exposure respectively. The Attest Rapid Readout biological indicator had 88%, 33%, and 0% enzyme activity detectable at 2, 3, and 4 minutes exposure. The chemical indicators Comply, Incheque, and Thermalog S revealed sterilization failure rates of 100%, 100%, and 100% at 0 minutes exposure; 100%, 100%, and 45% at one minute; 0%, 0%, and 28% at two minutes exposure; 0%, 0%, and 18% at three minutes exposure; and 0%, 0%, and 0% at four minutes exposure, respectively. CONCLUSION: The sensitivity of the Attest Rapid Readout parallels the conventional biological indicators. These data suggest that a 60-minute rapid readout biological indicator is equivalent to the 24-hour biological indicators. If further studies demonstrate that a four-minute flash sterilization cycle provides a needed safety margin to ensure sterilization, then consideration should be given to requiring a four-minute flash sterilization cycle. Chemical indicators were too sensitive to the processing conditions (eg, steam) and are inadequate to ensure adequate sterilization.

Evaluation Studies as Topic

Comparison of a rapid readout biological indicator for steam sterilization with four conventional biological indicators and five chemical indicators.

OBJECTIVE: In this study, we compare a new biological indicator that provides results within 3 hours with four conventional, 48-hour biological indicators and five chemical indicators. DESIGN: Biological indicators tested included the conventional Attest 1262, Proof Plus, Assert, and Biosign, and the new Attest 1292 Rapid Readout biological indicator. Chemical indicators tested included Comply, Propper, Chemdi, Sterigage, and Thermalog S. Spore survival following 121 degrees C in a gravity displacement sterilizer was measured by media color change after incubation for 24 and 48 hours at 56 degrees C for the conventional biological indicators, fluorescence at 3 hours for the Attest 1292 Rapid Readout biological indicator, and color change for the chemical indicators. Each exposure time was replicated 12 times with 5 samples of each indicator per run (ie, 60 replicates per indicator). RESULTS: At 48 hours, the conventional biological indicators Attest 1262, Proof Plus, Assert, and Biosign showed 100%, 95%, 88%, and 93% spore survival at 5 minutes' exposure 0%, 0%, 0% and 8% at 10 minutes; and all showed 0% survival at 15 minutes' exposure. Following a 3-hour incubation, the Attest 1292 Rapid Readout biological indicator showed fluorescence at 100%, 72%, and 0% at 5, 10, and 15 minutes, respectively. The chemical indicators Comply, Propper, Chemdi, Sterigage, and Thermalog S revealed sterilization failure rates of 100%, 100%, 100%, 100%, and 100% at 5 minutes' exposure; 0%, 0%, 0%, 92%, and 100% at 10 minutes; and 0%, 0%, 0%, 3%, and 27% at 15 minutes' exposure, respectively. CONCLUSIONS: The sensitivity of the Attest 1292 Rapid Readout biological indicator parallels that of conventional biological indicators. These data suggest that a 3-hour rapid readout biological indicator is equivalent to a standard 48-hour biological indicator. Some chemical indicators (eg, Thermalog S) failed to indicate adequate sterilization at 15 minutes' exposure. These chemical indicators have the potential of causing unnecessary recall of adequately sterilized items.

Equipment Contamination

[Inhalational exposure to rapidly eliminated substances: possibility and strategies for biological monitoring. A proposal for the use of biological limits equivalent to environmental limits].

Some advantages of biological compared with environmental monitoring and some preparatory steps and difficulties to be overcome during the planning of a biological monitoring program are firstly discussed. Then the biological compartments, their peculiarities and their use in the field of biological monitoring are described. The problem concerning the biological thresholds of the reference normal values and the biological limits corresponding to environmental limits (biological equivalent limits, BEL) is the next topic, followed by the description of the methods for measuring the BELs (in case of linear regression between biological and environmental values) and of the methods for the upper and lower confidence limits (UCL, LCL) of a biological value. They are to be used for a decision of compliance or noncompliance biological exposure. Finally some ways of using biological UCL-LCL and variation coefficients during cross-sectional and longitudinal studies (biological monitoring strategies) are shown.

Air Pollutants, Occupational

Biological UV dosimeters in the assessment of the biological hazard from environmental radiation.

To determine the impact of environmental UV radiation, biological dosimeters that weight directly the incident UV components of sunlight have been developed, improved and evaluated in the frame of the BIODOS project. Four DNA-based biological dosimeters ((i) phage T7, (ii) uracil thin layer, (iii) spore dosimeter and (iv) DLR-biofilm) have been assessed from the viewpoint of their biological relevance, spectral response and quantification of their biological effectiveness. The biological dosimeters have been validated by comparing their readings with weighted spectroradiometer data, by comparison with other biological doses, as well as with the determined amounts of DNA UV photoproducts. The data presented here demonstrate that the biological dosimeters are potentially reliable field dosimeters for measuring the integrated biologically effective irradiance for DNA damage.

Bacillus subtilis

Biological and immunological characterization of human luteinizing hormone: II. A comparison of the immunological and biological activities of pituitary extracts after electrofocusing using different standard preparations.

The profile of immunologically active human luteinizing hormone (hLH) was determined in aqueous pituitary extracts after electrofocusing using two radioimmunoassay systems and the estimates for each fraction were compared to those obtained by an in vitro bioassay method. Similar biological and immunological profiles were obtained in the pH 7.0-9.0 region, where most of the biological activity was present. Biological to immunological (B/I) ratios ranging from 0.6 to 1.7 (mean ratio 1.01; n = 21) were found in the major biologically active fractions of this pH region when a highly purified human pituitary LH preparation (68/40) was used as standard in both types of assays. The close proximity of these ratios to unity indicates a similar composition of biological and immunological activities in all these fractions in relation to that of the highly purified standard. However, marked discrepancies were observed in the pH region 3.0-7.0 where the B/I ratios ranged from 0.1 to 0.9, indicating the presence of immunological activity associated with relatively little biological activity. When impure human LH preparations of pituitary (69/104) and urinary (hMG 2nd IRP) origin were used as standards for the bioassay and radioimmunoassay of the hLH present in the major fractions of the pH region 7.0-9.0, significantly higher B/I ratios were obtained than with the use of the highly purified standard (68/40). These elevated B/I ratios are attributed to the presence in the impure standard preparations of immunological activity, which is associated with little or no biological activity. These observations may provide an explanation for the differences in B/I ratios which were reported for hLH in plasma, using different standard preparations.

Biological Assay

Biological and immunological characterization of human luteinizing hormone: IV. Biological and immunological profile of two international reference preparations after electrofocusing.

The first IRP of Human Pituitary Gonadotrophins (FSH/LH) for bioassay (69/104) and the 1st IRP of Human Pituitary Luteinizing Hormone (LH) for immunoassay (68/40) were fractionated by an electrofocusing technique in a sucrose density gradient and the profile of biological and immunological activities was determined. The partially purified LH preparation (69/104) gave a broad pattern of biolgical and immunological activities which extended from pH 4 to 10. The biological : immunological (B/I) ratio of the various fractions (using the 68/40 preparation as standard) ranged from 0.04 to 1.05. The low B/I ratios indicate the presence of high levels of immunologically active, biologically inactive material in this preparation. In contrast to the behaviour of the 69/104 preparation, the major proportion (88%) of the biological activity recovered after electrofocusing of the highly purified LH preparation (68/40) was found within the pH range 7--9, with B/I ratios (again using as standard the 68/40 preparation) ranging from 0.4 to 1.5. Multiple dose parallel line design radioimmunoassays revealed a lack of parallelism between the 69/104 and 68/40 International Reference Preparations. This was attributed to the presence of acidic material in the former preparation, which is practically absent from the latter. The biological LH profiles of both the 69/104 and 68/40 preparations differed from those previously reported for aqueous extracts of pituitaries. It is concluded that the dissimilarity in the electrofocusing profiles of the biological and immunological activities of the 69/104 preparation renders this preparation unsuitable as a reference preparation for the quantitation of biologically active LH by radioimmunoassay methods. Using the same criteria, the 68/40 preparation would appear to be a more suitable standard.

Animals

Biologically active luteinizing hormone (LH) in plasma. V. A re-analysis of the differences in the ratio of biological to immunological LH activities during the menstrual cycle.

The relationship between the biological and immunological activities of human luteinizing hormone (hLH) in plasma collected from female subjects was examined. The biological activity was measured by an in vitro bioassay and the immunological activity by an hLH radioimmunoassay (RIA), using improved reagents, such as the 1st IRP for human pituitary LH for immunoassay (code No. 68/40) as standard, a subunit-free biologically active iodinated hLH preparation as tracer and an anti-hLH serum of relatively high specificity. Similar profiles of biological (B) and immunological (I) activity were obtained in the plasma samples collected daily throughout 40 menstrual cycles (5 cycles from each of 8 subjects). However, the B/I ratios were significantly lower during the period of LH surge (P less than 0.001) than throughout the remainder of the cycle. The within- and between-assay variation in B/I ratios was investigated by the simultaneous assay of biological and immunological activities in plasma pools obtained by combining equal aliquots of plasma from each daily sample of the menstrual cycle from each of 5 cycles of each of 4 subjects. The analysis of these 20 pools revealed highly significant individual differences in B/I ratios, ranging from 0.81 to 1.33. The coefficient of variation was 20% between-subjects and 5% within-subjects. There was no seasonal variation in B/I ratios. That the individual differences in plasma B/I ratios were not attributable to the procedure of pooling was ascertained by the simultaneous assay of both activities in parellel in daily plasma samples and in the pools formed from these samples from three complete cycles. Thus the analysis of the differences in B/I ratios obtained throughout the menstrua- cycle revealed three major sources of variation. The first occurs in the form of generally elevated (higher than unity) B/I ratios, the second consists of a significant drop in B/I ratios during the midcycle LH surge, and the third source is represented by the significant between-subject differences. It is concluded that the first source is attributable to the relatively higher levels of "impurity" (i.e. biologically inactive, immunologically active material) in the standard preparation compared to those present in plasma of biologically inactive, immunologically active material of unknown composition and origin. If so, the latter source limits the quantitative significance of the RIA procedures employed. It is suggested that these three sources of variation account for most of the differences in B/I ratios for plasma lLH reported in the literature.

Adult

Reference values and human biological monitoring values for environmental toxins. Report on the work and recommendations of the Commission on Human Biological Monitoring of the German Federal Environmental Agency.

This article describes the working principles and working procedures of the Commission on Human Biological Monitoring, which was established in 1993 as a joint commission of the Federal Health Office (Bundesgesundheitsamt) and the Federal Environmental Agency (Umweltbundesamt) in Germany. One of the main tasks of the commission is to develop scientifically based criteria for the application of human biological monitoring and for the evaluation of human monitoring data in environmental medicine. In principle, two different kinds of criteria are recommended: (a) reference values and (b) human biological monitoring values (HBM values). Reference values are intended to indicate the upper margin of the current background exposure of the general population to a given environmental toxin at a given time. Reference values can be used to identify subjects with an increased level of exposure (in relation to background exposure) to a given environmental toxin. However, reference values do not represent health-related criteria for the evaluation of human biological monitoring data. HBM values are derived from human toxicology and epidemiology studies and are intended to be used as a basis for a health-related evaluation of human biological monitoring data. Usually the commission recommends two different HBM values: HBM I, the concentration of an environmental toxin in a human biological material (usually blood, serum, plasma, or urine) below which there is--according to the knowledge and judgement of the commission--no risk for adverse health effects in individuals of the general population: and HBM II, the concentration of an environmental toxin in a human biological material (usually blood, serum, plasma, or urine) above which there is--according to the knowledge and judgement of the commission and with regard to the environmental toxin under consideration--an increased risk for adverse health effects in susceptible individuals of the general population. The HBM I value can be considered a kind of alert value (from the toxicological point of view), whereas the HBM II value represents a kind of action level, at which attempts should be undertaken to reduce the level of exposure immediately and to carry out further medical examinations. Values between HBM I and HBM II should be considered a warning signal of the need to control the analytical measurement and to reduce the level of exposure of the concerned individual as reasonably as is achievable. At present, reference and HBM values are available for lead in blood, for cadmium and mercury in blood and urine, and for pentachlorophenol in plasma/serum and urine. Reference values have been established for some polychlorinated biphenyls in blood and plasma as well as for hexachlorocyclohexane and hexacholorobenzene in blood as well as for some organochlorine in human milk.

Adolescent

Methodological problems in evolutionary biology. VIII. Biology and culture.

Biology cannot accommodate all aspects of culture. Aspects of culture that a biological approach can take into account can be covered by the biological categories of "phenotype" and "environment". There is no need to treat culture as a separate category. Attempts to elaborate biological explanations of "cultural variation" will meet with success only if biologists expand theories of development, and integrate them in evolutionary biology. The alternative--elaborating the idea of so-called "cultural inheritance"--makes little sense from a biological point of view.

Animals

Biological control. Aspects of biological control--with special reference to arthropods, protozoans and helminths of domesticated animals.

Biological control describes situations in which a living antagonist (a predator, parasite, parasitoid or a pathogen) is distributed by man to lower pest (parasite) populations to acceptable sub-clinical densities or to keep the population at a non-harmful level. Ideally, biological control has no negative effects on the environment, whereas chemical control is not always so harmless. Laboratory and field observations have revealed many organisms, such as viruses, bacteria, fungi, protozoans, turbellarians, nematodes, earthworms, tardigrades, insects, copepods and mites as antagonists to parasitic arthropods, protozoans and helminths of domesticated animals. However, only very few of these antagonists have shown promising qualities as biological control agents within veterinary science. The lack of success should be linked to the lack of knowledge about complex natural biological systems and the antagonists that may be found there. This situation has restricted the interest of industry in developing biological products. In the future, however, industry may become more interested in biological control considering the increasing problems with parasite resistance to drugs in combination with the increasing cost of developing new chemical products, and because of increasing public concern about chemical residues in animal products and in the environment.

Animals

Hierarchical functional organization of formal biological systems: a dynamical approach. I. The increase of complexity by self-association increases the domain of stability of a biological system.

In this series of papers, a theory of functional organization is proposed for biological systems (formal biological system, FBS), which is based on the concept of 'functional interaction', and on a 'functional self-association hypothesis'. From the specific properties of functional interactions, i.e. non-symmetry, non-locality, and non-instantaneity, it is shown that a biological system can be considered as constituted by two hierarchical systems: (i) the (O-FBS) that describes the topology of the FBS, i.e. the functional organization, with a hierarchical directed graph; (ii) the (D-FBS) that describes the continuous non-linear dynamics of the FBS with a field. In the framework of this theory, the problem of the relation between structure and function is considered to be due to the distinction between structural organization and functional organization. Some advantages of this approach are: (i) the description of the time evolution, during development, of the organization of an FBS with an optimum principle, which leads to a clear comparison with a physical system (paper II); (ii) the description of the space-time dynamics as the variation in space and time of field variables in a hierarchical 'space of structural units'; and, consequently, the relation between topology and geometry, and the existence of non-locality in these hierarchical spaces (paper III). In this paper, the basic concepts of functional interaction, hierarchical functional organization, and physiological function are discussed from a mathematical viewpoint, and arguments for the validity of the self-association hypothesis are given. Specifically, it is shown that, for a particular class of biological systems that are taken as an example, the domain of stability of the (D-FBS) is increased after functional association. This property, which is specifically due to the nature of the biological system, corresponds to an increase in complexity. It will be shown in the second paper that such a self-organization corresponds also to an optimal principle for the (O-FBS). The case of real biological systems (RBSS) is considered in relation with the present theory, which leads to a new hierarchical representation in terms of fields. Such representation could be a base for integrative physiology. As an example, some physiological functions, respiratory and cardio-vascular, are considered and it is shown that the heart shock emerges from the formulation as a cyclic sub-graph.

Animals

Biologicals and biological response modifiers: fourth modality of cancer treatment.

Considerable progress has been made in the last 5 years toward the development of specific biological approaches to the treatment of cancer. The techniques of genetic engineering, mass cell culture, and improved techniques in protein and nucleic acid sequencing and synthesis have made available biologicals as specific, highly purified molecules that can be used in cancer therapy. While extensive clinical trials are needed to demonstrate that biologicals and biological response modifiers can provide a survival advantage for patients with cancer, the preliminary data indicate that these approaches can be useful in inducing responses in patients with clinically apparent disease. Further studies with these approaches in conjunction with surgery, radiotherapy, and chemotherapy should be helpful in definitively establishing biologicals and biological response modifiers as the fourth modality of cancer treatment.

Adjuvants, Immunologic