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Managing Recreational Trail Environments for Mountain Bike User Preferences.

/ The carrying capacity model is an effective tool for the management of a wildland recreation resource. Within the model are four primary subcapacities, namely, physical capacity, biological capacity, social capacity, and facility capacity; combined, they are essential to the appropriate management of wildland recreation resource environments. This study focuses on environmental factors of recreational environments that are primarily used by mountain bikers. Little research has been conducted on the social carrying capacity of mountain biking environments, relative to the amount of physical and biological capacity research that has been conducted. The objective of this study was to further resource management knowledge of the mountain bike user in order to better incorporate social carrying capacity into the management of bike use environments. An email survey was used to identify such issues as mountain biker preference of soil erosion management techniques and to measure the effect on experience of resultant factors of soil erosion and trail design. Other issues, such as environmental concern, biker perception of other users, and biker commitment, were also measured. A 58% response rate was achieved. Data gathered from bikers in the United States, United Kingdom, Australia, and New Zealand (N = 406), highlight some important issues concerning the design and management of wildland recreation environments that are primarily used for mountain biking. For example, bikers were found to significantly prefer water bars above all other tested soil erosion management techniques; trail erosion factors, including the presence of rocks, roots, and gullies, all added to biking experiences on average; trail design factors, such as the presence of turns, bumps, jumps, and obstacles, all added to biking experiences in general. These findings were used to address questions that resource managers should consider when striving to effectively manage wildland recreation areas primarily used for mountain biking.

Journal Article↗

Resource pulses, species interactions, and diversity maintenance in arid and semi-arid environments.

Arid environments are characterized by limited and variable rainfall that supplies resources in pulses. Resource pulsing is a special form of environmental variation, and the general theory of coexistence in variable environments suggests specific mechanisms by which rainfall variability might contribute to the maintenance of high species diversity in arid ecosystems. In this review, we discuss physiological, morphological, and life-history traits that facilitate plant survival and growth in strongly water-limited variable environments, outlining how species differences in these traits may promote diversity. Our analysis emphasizes that the variability of pulsed environments does not reduce the importance of species interactions in structuring communities, but instead provides axes of ecological differentiation between species that facilitate their coexistence. Pulses of rainfall also influence higher trophic levels and entire food webs. Better understanding of how rainfall affects the diversity, species composition, and dynamics of arid environments can contribute to solving environmental problems stemming from land use and global climate change.

Biodiversity↗

Demographic consequences of age-structure in extreme environments: population models for arctic and alpine ptarmigan.

Organisms living in arctic and alpine environments are increasingly impacted by human activities. To evaluate the potential impacts of global change, a better understanding of the demography of organisms in extreme environments is needed. In this study, we compare the age-specific demography of willow ptarmigan (Lagopus lagopus) breeding at arctic and subalpine sites, and white-tailed ptarmigan (L. leucurus) breeding at an alpine site. Rates of egg production improved with age at the alpine and subalpine sites, but the stochastic effects of nest and brood predation led to similar rates of annual fecundity among 1-, 2-, and 3+-year-old females. All populations had short generation times (T<2.7 years) and low net reproductive rates (R0<1.2). Stable age distributions were weighted towards 1-year-old females in willow ptarmigan (>59%), and to 3+-year-old females in white-tailed ptarmigan (>47%). High damping ratios (rho>3.2) indicated that asymptotic estimates were likely to match natural age distributions. Sensitivity and elasticity values indicated that changes in juvenile survival would have the greatest impact on the finite rate of population change (lambda) in willow ptarmigan, whereas changes to the survival of 3+-year-old females would have a greater effect in white-tailed ptarmigan. High survivorship buffers white-tailed ptarmigan in alpine environments against the potential effects of climate change on annual fecundity, but may make the species more sensitive to the effects of pollutants or harvesting on adult survival. Conversely, processes that reduce annual fecundity would have a greater impact on the population viability of willow ptarmigan in arctic and subalpine environments. If these same demographic patterns prove to be widespread among organisms in extreme environments, it may be possible to develop general recommendations for conservation of the biological resources of arctic and alpine ecosystems.

Age Distribution↗

Chemical composition of smoke produced by high-frequency electrosurgery in a closed gaseous environment. An in vitro study.

BACKGROUND: High-frequency (HF) electrocoagulation and cutting procedures produce smoke by high-temperature pyrolysis of tissues. As distinct from the experience of conventional surgery, electrosurgical smoke is produced in a closed gaseous environment during laparoscopic operations. As a result, toxic chemicals may be absorbed into the circulation. The effects of this absorption are not known. Furthermore, the chemical composition of electrosurgical smoke produced in an anoxic environment may be different from that produced in air. METHODS: Smoke was produced in vitro by HF electrocutting of fresh porcine liver in helium, CO2, and air-saturated closed environments. Smoke samples were collected and analyzed by gas chromatography-mass spectrometry (GC-MS). RESULTS: The chemical constituents of electrosurgical smoke produced in air, CO2, and helium were similar. To date, 21 chemicals, some highly toxic, have been identified in the electrosurgical smoke produced in a closed environment. These consist of hydrocarbons, nitriles, fatty acids, and phenols. CONCLUSIONS: Electrosurgical smoke produced in a closed environment contains several toxic chemicals. The effects of these on cell viability, macrophage, and endothelial cell activation are not known but are being investigated. Meantime, measures to reduce smoke and evacuate it during endoscopic surgery are advisable.

Air Pollutants↗

Heavy metal contamination and distribution in the urban environment of Guangzhou, SE China.

Ever-increasing heavy metal accumulation in the urban environment of Guangzhou, the largest light industrial production base and one of the most rapidly developing cities in China, poses a serious threat to environment as well as to human health in the region. As a sink or source, urban deposits are good indicators of the level and extent of heavy metal accumulation in the surface environment. The aim of this preliminary study was to examine the distribution of heavy metal contamination in the urban environment of Guangzhou. It was based on a systematic sampling of road dusts and corresponding gully sediments along major roads running mainly through commercial and residential to industrial districts of the city. In addition to road dusts and gully sediments, ceiling dusts from the Pearl River Tunnel were also collected to characterize anthropogenic emissions dominated by traffic-related activities. In general, the level of Cd, Cu, Pb and Zn contaminations were more severe on the industrialized side of Guangzhou than on the western side where heavy traffic and industrial activities were limited. The primary determinants of the level of heavy metal contamination and the distribution of this contamination in the urban environment of Guangzhou were the site-specific conditions of its urban setting, particularly the types of industries, the nature of the traffic flow, sample residence times and variations in grain size of the particulate contaminants. This study highlights the complexity of the urban system and indicates that in just such a system individual urban components should be interlinked to assess the long-term environmental and health effects of heavy metal contamination. Among the heavy metals tested--Cd, Cu, Pb and Zn--the level of Zn contamination was the most severe and widespread, and thus requires immediate attention.

China↗

Determination of anesthetic molecule environments by infrared spectroscopy. II. Multiple sites for nitrous oxide in proteins, lipids, and brain tissue.

The presence of molecules of the general anesthetic nitrous oxide (N2O) in oils, esters, proteins, red cells, cream, lipid vesicles, and brain tissue upon exposure to the gas was observed by infrared spectroscopy. Analysis of the N-N-O antisymmetric stretch band reveals a distribution of N2O molecules among several sites of differing polarity in these solutions and tissues. The sensitivity of the band intensity and frequency to the number and strength of the dipoles in the solvating molecules is demonstrated by the resolution of N2O-ester and N2O-alkane interactions in acetic acid ethyl ester and oleic acid methyl ester. In all aqueous solutions and in all tissues a population of N2O molecules in water is observed. At least two sites of N2O-protein interaction are observed in purified hemoglobin A and packed red cells; multiple N2O sites may also be present in bovine serum albumin. Two sites of N2O-lipid interaction are observed in whipping cream and in an aqueous suspension of phosphatidylcholine vesicles. The sites providing the least polar immediate environment to N2O in hemoglobin, cream, and vesicles give similar band frequencies to those found in pure alkane solvents. Infrared spectra of bovine brain tissue, upon exposure to N2O, show N2O molecules present in water and in two less-polar environments. Analysis of spectra of N2O in cerebellum tissue removed from a dog under halothane-N2O anesthesia reveals, in addition to N2O in water, a single population of N2O molecules in an alkane-like environment. Infrared spectroscopy provides a unique means of probing the structure of the environment of N2O and should prove useful in correlating anesthetic potency with anesthetic environment under physiological conditions.

Animals↗

A source inventory and budget for chlorinated dioxins and furans in the United Kingdom environment.

Polychlorinated dibenzo-p-dioxins (PCDDs) and -furans (PCDFs) are ubiquitous in the environment. This paper estimates the present UK environmental loading of PCDD/Fs in soils, vegetation, air, water and sediments. Greater than 95% of the estimated total PCDD/F loading of 5.7 t in the UK environment is present in surface soils. Annual emissions from known primary sources of PCDDs and PCDFs are estimated. The most important of these include: municipal waste incinerator stack emissions (10.9 kg sigma PCDD/F per annum); industrial (7.7 kg/year) and domestic (5.1 kg/year) combustion of coal; clinical waste incinerators (1.7 kg/year); volatilisation from chlorophenol-treated substrates (1.7 kg/year) and combustion of leaded petrol by motor vehicles (0.7 kg/year). These sources are generally easy to define and reasonably reliable national estimates can be obtained. More difficult to quantify are secondary releases from the large UK stock of pentachlorophenol (PCP) and PCP-treated products, which may represent quantitatively one of the most important sources of total PCDD/Fs to the environment. Estimates of homologue-specific emissions indicate that combustion processes represent a far more significant source of tetra and penta CDD/Fs than do chlorophenols, which in turn constitute a greater source of hepta- and octachlorinated congeners. Direct emission of PCDD/Fs into the atmosphere from combustion processes facilitates their atmospheric transport to remote locations. This, coupled with the diffuse nature of combustion processes, means that the effects of PCDD/F contamination originating from anthropogenic combustion are more widespread than those from the use and disposal of chlorophenols. Contamination from chlorophenols will be more localised, owing to the insignificance of direct atmospheric release pathways for this source. Although there is reasonable agreement between the estimated current annual flux and the present UK environmental loading of PCDDs and PCDFs, a large discrepancy exists between the sum of the annual contributions from primary sources and this annual flux. Whilst the existence of an as yet unidentified source or sources or gross underestimates of known sources cannot be excluded, it is proposed that much of this discrepancy may be accounted for by secondary releases from the use and disposal of chlorophenols and the long-range transport, continued remobilisation and subsequent redeposition of PCDDs and PCDFs already present in the environment. Despite limited evidence for a modest decline in levels of PCDDs and PCDFs in some environmental compartments over the last 20 years, the environmental persistence of these chemicals means that they will remain in the UK environment for the foreseeable future despite recent action to curb primary emissions.

Air Pollutants↗

Polychlorinated biphenyls (PCBs) in the British environment: sinks, sources and temporal trends.

This paper estimates the present UK environmental loading of polychlorinated biphenyls (PCBs). Of the estimated approximately 40,000 t SigmaPCB sold in the UK since 1954, only an estimated 1% (400 t) are now present in the UK environment. Comparisons of estimated production and current environmental loadings of congeners 28, 52, 101, 138, 153 and 180 suggest that PCB persistence broadly increases with increasing chlorination. Those PCBs that are not now present in the UK environment are considered to have been destroyed--by natural or anthropogenic mechanisms, to be still in use, to reside in landfills or to have undergone atmospheric and/or pelagic transport from the UK. The dramatic fall in PCB levels in archived UK soils and vegetation between the mid-1960s and the present is evidence that the latter mechanism is the most important and that a significant proportion of PCBs released into the UK environment in the 1960s have subsequently undergone environmental transport away from the UK. The bulk (93.1%) of the estimated contemporary UK environmental burden of SigmaPCBs is associated with soils, with the rest found in seawater (3.5%) and marine sediments (2.1%). Freshwater sediments, vegetation, humans and sewage sludge combined account for 1.4% of the present burden, whilst PCB loadings in air and freshwater are insignificant. Although consideration of individual congeners does not reveal any major deviations from the relative partitioning of Sigma PCBs, the importance of sinks other than soils is enhanced for individual congeners, particularly 138 and 180. In particular, around 2% of the total UK burden of congener 180 is present in humans, implying that biodata as a whole may constitute an important sink for the higher chlorinated congeners. The contemporary flux of SigmaPCBs to the UK surface is estimated at 19 t yr(-1), compared with an estimated annual flux to the atmosphere of 44-46 t. This implies that the major sources of PCBs to the UK atmosphere have been identified and that there is currently a net loss of these compounds from the UK. These sources are: volatilisation from soils (88.1%), leaks from large capacitors (8.5%), the production of refuse-derived fuel (RDF) (2.2%), leaks from transformers (0.6%), the recovery of contaminated scrap metal (0.5%) and volatilisation from sewage sludge-amended land (0.2%). Interestingly, whilst large excesses of estimated annual fluxes to the atmosphere over deposition fluxes for individual congeners exist for congeners 28, 52 and 101, estimates of fluxes in both directions across the soil-atmosphere interface agree closely for congeners 138, 153 and 180. This suggests that lower chlorinated congeners are more susceptible to both long-range environmental transport beyond the UK and to atmospheric degradation. Retrospective analysis of dated sediment cores, vegetation and soils indicates that environmental transport from North America and continental Europe introduced PCBs into the British environment well before the onset of their commercial production in the UK in 1954. Since that time, the input of PCBs to the UK environment has essentially reflected temporal trends in UK use. After peaking in the 1960s they declined rapidly through the 1970s following restrictions on PCB use. Recent evidence, however, is that the rate of decrease has diminished and that further significant reductions in fresh environmental input will take some time to occur. Such reductions will be especially slow for humans and other biota with long life-spans. This stems partly from cross-generational transfer from parents to offspring and also because the persistence of PCBs in biota means that present body burdens will reflect past as well as current exposure.

Journal Article↗

A concept for detecting unexpected changes in the environment early.

A project was established under the auspices of the German Federal Ministry of Research and Technology with the task of developing a concept for the early recognition of signals for unexpected deleterious changes in the environment. Predictive assessments of products (e.g., chemicals) and technologies as regards their potential environmental impacts contain numerous sources of error and uncertainties. Therefore, appropriate observation systems are needed in order to detect unexpected developments in the environment and in human health. Long-term storage of samples (environmental specimen banking) is the third basic activity that must be undertaken within an early warning system. When monitoring the environment for unwanted changes, it is not sufficient to trace some individual agents, preselected for their well-known capacity to inflict harm. The following avenues of identifying symptoms of change in the environment were identified: development and deployment of "key indicators"; acquisition and correlative treatment of conventional monitoring data from different sources; and execution of concise studies in environmental problem areas. Key indicators are defined as scientific measurement and observation methods which respond to early stages of anthropogenically induced environmental changes and are capable of responding to a multitude of simultaneously present agents. A series of examples is discussed. Approaches concerning how the statistical evaluation of available sets of environment-related data could reveal unexpected developments are presented.

Biosensing Techniques↗

Evaluation of glucose controllers in virtual environment: methodology and sample application.

OBJECTIVE: Adaptive systems to deliver medical treatment in humans are safety-critical systems and require particular care in both the testing and the evaluation phase, which are time-consuming, costly, and confounded by ethical issues. The objective of the present work is to develop a methodology to test glucose controllers of an artificial pancreas in a simulated (virtual) environment. MATERIAL AND METHODS: A virtual environment comprising a model of the carbohydrate metabolism and models of the insulin pump and the glucose sensor is employed to simulate individual glucose excursions in subjects with type 1 diabetes. The performance of the control algorithm within the virtual environment is evaluated by considering treatment and operational scenarios. RESULTS: The developed methodology includes two dimensions: testing in relation to specific life style conditions, i.e. fasting, post-prandial, and life style (metabolic) disturbances; and testing in relation to various operating conditions, i.e. expected operating conditions, adverse operating conditions, and system failure. We define safety and efficacy criteria and describe the measures to be taken prior to clinical testing. The use of the methodology is exemplified by tuning and evaluating a model predictive glucose controller being developed for a wearable artificial pancreas focused on fasting conditions. CONCLUSION: Our methodology to test glucose controllers in a virtual environment is instrumental in anticipating the results of real clinical tests for different physiological conditions and for different operating conditions. The thorough testing in the virtual environment reduces costs and speeds up the development process.

Algorithms↗

Fluorescence spectroscopic studies to characterize the internal environment of tetraethyl-orthosilicate derived sol-gel bulk and thin films with aging.

Characterization of the internal environment of a sol-gel matrix is an important area of investigation in optical biosensors. In the present study, different sol-gel compositions were prepared by varying the water (H2O) to tetraethyl-orthosilicate (TEOS) ratio (R) from 1 to 16 and the changes in the internal environment of the sol-gel both in bulk and thin films as a function of aging (storage) were investigated using fluorescence spectroscopy. We focussed on the fluorescence characteristics , viz. emission and excited state lifetime of Hoechst 33258 (H258), a bisbenzimidazole derivative, which was used as fluorescence probe entrapped in the TEOS derived sol-gel bulk and thin films. These sols were prepared at a low pH (approximately 2.0) and the thin films were coated by dip coating technique at withdrawal speeds of 1 cm/min and 0.1cm/min. Usually, uniform thin films were obtained at a high speed (1 cm/min) and partially cracked film at a low speed (0.1 cm/min) as observed by fluorescence microscope. These observations did not change during aging. On the contrary, three months long observations on steady-state fluorescence emission measurements on H258 depicted a blue shift from 535 nm to 508 nm at R = 1 in the sol-gel bulk, whereas at higher ratios this was not prominent. At all ratios, dual emission bands were observed in thin films. This may be due to faster sol-gel to xerogel transition during aging depending on the ratio (R). Analysis of the excited state decay profiles of H258 revealed a double exponential fitting having a short (tau1) and a long (tau2) component in both fresh and during aging, in the sol-gel bulk and thin films, indicating heterogeneity in the internal environment. The value of tau1 increased from 0.4 ns to 1.2 ns whereas tau2 attained a value from 3.0 ns to 3.6 ns at R = 1 upon aging in the sol-gel bulk. The corresponding values of tau1 and tau2 in thin films were 0.3 ns and 3.5 ns, respectively. The values of these decay components in thin films did not alter much due to storage, but their relative contributions showed more systematic changes in the thin films. The observed changes could be correlated to rigidification in the bulk depending on the ratio (R). This process was very slow at R > or = 4. The heterogeneity in the internal environment of bulk and thin films upon aging appeared to be different as revealed from analysis of excited-state lifetime. Thus, the bisbenzimidazole derivative H258 appears to be very useful probe for characterizing the internal environment of both the sol-gel bulk and thin films.

Luminescent Measurements↗

The relationships of dissociation and affective family environment with the intergenerational cycle of child abuse.

OBJECTIVE: The purpose was to test a model that may explain how physically abused children become physically abusive parents. It was predicted that when the family's affective environment is uncohesive, unexpressive, and conflictual, a history of abuse experiences would be associated with elevated dissociation. It was hypothesized that dissociation would mediate between a childhood history of abuse and the current potential to be physically abusive. METHOD: Abuse history, affective environment in the family-of-origin, dissociation, and abuse potential were assessed in a sample of 76 mothers with elementary school-age children. RESULTS: Predictions were supported. Affective Family Environment moderated the relation between abuse history and dissociation, with abuse history relating to greater dissociation primarily when the family environment was conflictual, uncohesive and unexpressive. Further, dissociation significantly mediated the relation between abuse history and abuse potential (Z = 2.19, p < .05). CONCLUSIONS: Dissociation's strong association with abuse potential may partially explain why only some abused children later perpetuate the cycle of abuse, as those who are not dissociative into adulthood are likely to have lower abuse potential, in contrast to those displaying elevated dissociation. The extent of the dissociation may depend on the affective family environment in which the abuse took place.

Adult↗

A test battery for the ecotoxicological evaluation of the agri-chemical Environ.

The ecotoxicological effects of the agri-chemical Environ were evaluated using a test battery comprising organisms representing three trophic levels of the aquatic ecosystem. The sensitivities of the test species to Environ were as follows: Microtox > Daphnia magna > Pseudokirchneriella subcapitata = Thamnocephalus platyurus = Oncorhynchus mykiss > Artemia salina > Tetrahymena thermophilia. An order of magnitude sensitivity between the test species was observed which emphasizes the importance of a test battery approach in the assessment of possible ecological consequences of agri-chemicals. In addition, the aquatic bioassays were found to be more sensitive (e.g., greater than three orders of magnitude for D. magna) than previously reported mammalian toxicity data for Environ. Toxicity of Environ was also investigated using fish (RTG-2) and human fibroblast cell lines (HepG2 cells) and juvenile O. mykiss. Environ was shown to have greater toxicity in the acute lethality test than with the fish cell line. However, in vivo/in vitro comparisons in this instance we feel would be premature and imprecise owing to valid concerns regarding fish loading rates for the in vivo test, and exposure duration with the in vitro test.

Agrochemicals↗

Twin differences in birth weight: the effects of genotype and prenatal environment on neonatal and post-neonatal mortality.

There is much evidence to suggest that both genes and prenatal environment influence life chances. However, recent within-twin estimates also raise questions about how the influence of genes and prenatal environment may vary across different subgroups of a population and over time. This paper explores such potential variation within the 1st year of life. Using data on twin births from the 1995-1997 Matched Multiple Birth Database and an analytic strategy based on the Weinberg assumption, this paper considers how associations between birth weight and infant mortality vary across identical and fraternal twins, gestational age, and time. Results suggest that the influence of genes and prenatal environment vary most significantly by gestational age. In pregnancies that lasted less than 37 weeks, within-twin variation in prenatal environment is able to account for negative associations between birth weight and infant mortality. However, in pregnancies that lasted 37 weeks or longer, underlying genetic variation across fraternal twins appears to be largely responsible for birth weight-mortality associations. Such distinct findings by gestation suggest that genes and prenatal environment may play varying roles in birth weight-mortality associations across different situations.

Birth Weight↗

Characterization of aerosols and its radiative impacts over urban and rural environments--a case study from Hyderabad and Srisailam.

In the troposphere anthropogenic aerosol emissions are increasing in recent decades, which can influence the earth's climate. The present study addresses the characterization of aerosols and their radiative impacts over urban (Hyderabad) and rural (Srisailam) environments by using aerosol optical depth (AOD) measurements from MICROTOPS-II sunphotometer. AOD measurements over the urban site showed high values compared to the rural site. Over the urban environment aerosol forcing at the surface is as high as -42 W m(-2) and at the top of the atmosphere (TOA) is +10 W m(-2) whereas at the rural environment aerosol forcing at the surface has been observed to be -11 W m(-2) and at TOA it is observed to be +5.7 W m(-2). The difference between TOA and the surface forcing over the urban environment is +32 W m(-2) and over the rural environment is +5.3 W m(-2), which shows the absorption capacity of the respective atmospheres.

Aerosols↗

Modulation of IFN-gamma production by TNF-alpha in macrophages from the tumor environment: significance as an angiogenic switch.

BACKGROUND: The role of macrophages in tumor angiogenesis has been known to influence in the production of angiogenic cytokines and growth factors including TNF-alpha. Recently, macrophages were also found to produce INF-gamma, which were found to be involved in angiogenic inhibition. Thus, the importance of macrophages in tumor angiogenesis might be the angiogenic switch. The hypothesis tested here is that TNF-alpha can modulate the INF-gamma production in macrophages in tumor environment as part of the tumor angiogenic switch. METHODS: Macrophages in tumor environment were obtained from peritoneal cavity and s.c. grown tumor of C57BL/6 mice injected with B16F10 melanoma cell line for 6 and 11 days, respectively. Mac1+-macrophages were purified using magnetic beads (MACs; Milteny Biotech, Germany) and cultured with various concentrations of TNF-alpha at various time points at 37 degrees C. The supernatants were analyzed for IFN-gamma or VEGF by ELISA kit. RESULTS: Residential macrophages from peritoneal cavity did not respond to LPS or TNF-alpha to produce INF-gamma. However, the cells from tumor environment produced IFN-gamma as well as VEGF. Upregulation of IFN-gamma production by the addition of LPS or TNF-alpha was observed in macrophages from the tumor bearing peritoneal cavity. RT-PCR analysis revealed external TNF-alpha-induced IFN-gamma gene expression in macrophages from tumor environment. CONCLUSION: The overall data suggest that the macrophages in tumor environment might play an important role not only in angiogenic signal but also in anti-angiogenic signal by producing related cytokines. Moreover, TNF-alpha might be a key cytokine functioning as a tumor angiogenic switch.

Animals↗

Setting times of Resilon and other sealers in aerobic and anaerobic environments.

Eleven sealers, including Resilon sealer, were mixed according to manufacturer's instructions. Setting times were determined in both aerobic and anaerobic environments. Two samples of each sealer were mixed and placed in the following conditions: (a) uncovered in an aerobic incubator; (b) covered with a glass cover-slip in the aerobic incubator; (c) covered with phosphate buffered saline in an aerobic incubator; (d) uncovered in an anaerobic incubator; (e) light cured and then placed in the aerobic incubator (Resilon only). All samples were tested for setting times with a Gillmore needle at 15, 30, and 60 minutes, then hourly up to 8 hours, then at 24, 48, and 72 hours, and then weekly up to 3 weeks. Ketac Endo and Kerr Tubliseal, were the fastest sealers to set in aerobic environments. Ketac Endo and Resilon were the fastest sealers to set in anaerobic environments. Roth 801 and Roth 811 were the slowest sealers to set, taking over 3 weeks to set in either anaerobic or aerobic environments. Resilon sealer set in 30 minutes in both anaerobic environments. However, in the presence of air, Resilon took a week to set and when placed in PBS, an uncured layer remained on the surface.

Aerobiosis↗

Direct compression as an appropriately mechanical environment in bone tissue reconstruction in vitro.

Determining how to apply an appropriately mechanical environment which can improve the quality and function of bone-like construct in vitro is a required problem to be solved for the current development of bone tissue engineering. A specific mechanical force may be a key determinant of tissue development in vitro in bone tissue engineering. From the standpoint of bionics, the mechanical environments applied on bone tissue engineering should work in three aspects: providing adequately mechanical stimuli to the cells seeded in 3-D scaffold; ensuring the efficient mass-transport of the nutrients and waste products of the cells; promoting the development of functionally extracellular matrix in 3-D scaffold. After the analysis of several differently mechanical environments comparing with that in vivo, the directly dynamical compression environment, instead of hydrostatic pressure or microgravity or direct perfusion, can recreate the in vivo mechanisms of mechanosensation, mechanotransduction and mass-transport during engineered bone-like tissue culturing process in vitro. Therefore, it is hypothesized that the directly dynamic compression will be a specific mechanical environment to bone tissue reconstruction in vitro.

Bone and Bones↗