Serologically defined Rhipicephalus (Boophilus) microplus larval antigens in BmLF3, a partially pure Sephacryl S-300 fraction of crude larval proteins

This report is designed to provide additional information regarding larval soluble proteins toward the planned development of a comprehensive database of Rhipicephalus (Boophilus) microplus proteins that elicit a humoral immune response in cattle as a result of natural ectoparasite infestation. Larval proteins of R. microplus are complex and the protein profile is not dominated by any major proteins. This report focuses upon an S-300 Sephacryl (molecular sieve) column fraction, fraction 3 (BmLF3). With the use of SDS-PAGE (without-2ME) and Western blotting with a composite pool of pre- and post-R. microplus larval infestation antiserum BmLF3 was found to contain 7 apparent common ixodid major antigens (207.3, 171.9, 98.0, 86.5, 65.7, 58.9, and 38.0 kDa), those potentially shared with other ixodid species, and 2 apparent R. microplus specific antigens evidenced by low-level antibody binding in crude BmLF3 (149.4 kDa) and HPLC peak 8 of BmLF3 (116.0 kDa). In addition, BmLF3 contains potent inhibitors of trypsin activity. However, these inhibitors of trypsin did not appear to elicit host antibodies as a result of natural ectoparasite exposure, as defined by Western blotting of reduced and denatured trypsin binding proteins purified by affinity chromatography.     

Evaluating the public health response to a mass bat exposure—Wyoming, 2017

Mass bat exposures (MBEs) occur when multiple people are exposed to a bat or a bat colony, often over an extended period. In August 2017, a public health investigation was started in response to an MBE that occurred during May–August 2017 at a national park research station in Wyoming. We identified 176 people who had slept primarily in two lodges (Lodges A and B) at the research station, and successfully contacted 165 (93.8%) of these individuals. Risk assessments (RAs) were administered to all 165 individuals to determine degree and type of exposures to bats (e.g., biting or scratching). Exposure status for research station guests was classified as “non‐exposed,” “low risk” or “high risk,” and counselling was provided to guide post‐exposure prophylaxis (PEP) recommendations. Prior to public health notification and intervention, 19 persons made the decision to pursue PEP. The healthcare‐seeking behaviours of this group were taken to represent outcomes in the absence of public health intervention. (These persons received a RA, and their risk classification was retrospectively assigned.) Approximately 1–2 weeks after conducting the RAs, we conducted a follow‐up survey to determine whether recommendations regarding PEP were ultimately followed. The proportion of individuals that unnecessarily pursued PEP was higher among the 19 individuals that sought health care prior to receiving the RA (p < 0.00001). Among those receiving the RA first, all persons classified as high risk followed public health guidance to seek PEP treatment. Despite this, upon re‐interview, only 21/79 (26.6%) of guests could accurately recall their risk classification, with most people (55.7%) overestimating their risk. Study findings demonstrate that early public health interventions such as RAs can reduce unnecessary use of PEP and that messaging used during rabies counselling should be clear.     

Effects of chronic hypobaric hypoxia exposure on dendritic spine morphological changes and filamin-A expression in neurons of mouse hippocampal CA1 region

AIM:To investigate the effects of hypobaric hypoxic exposure on the morphological changes of dendritic spines and the expression of filamin-A in the neurons of mouse hippocampal CA1 region. METHODS:C57BL/6 male mice (6~8-week-old) were divided into normoxia 7 d group, normoxia 14 d group, hypobaric hypoxia 7 d group and hypobaric hypoxia 14 d group. The mice in hypobaric hypoxia exposure groups were placed in a hypobaric chamber with hypobaric hypoxia exposure to simulate the plateau at an altitude of 6 000 m. Golgi staining assay was used to observe the branch number of dendrites, and the length and density of basal and apical dendritic spines in the hippocampal CA1 region. The protein expression of filamin-A in the hippocampus of the mice was determined by Western blot. The protein expression and distribution of filamin-A in the hippocampal CA1 region were detected by immunofluorescence staining. RESULTS:Compared with normoxia exposure group, no significant difference of the number of dendritic branches in the hippocampal CA1 region after hypobaric hypoxia exposure was observed. However, the length of basal spines and apical spines was increased significantly (P<0.05), and the density of basal spines and apical spines was significantly reduced after hypobaric hypoxia exposure (P<0.01). The results of Western blot showed that the protein expression of filamin-A in the hippocampus of the mice after hypobaric hypoxia exposure was lower than that in normoxia exposure group (P<0.01 or P<0.05). Immunofluorescence staining showed that the filamin-A protein was expressed in the mouse hippocampal CA1 region, and the expression level after hypobaric hypoxia exposure was lower than that in normoxia group. CONCLUSION:Chronic hypobaric hypoxia exposure affects the protein expression level of filamin-A in the mouse hippocampal CA1 region, thus leading to the morphological changes of dendritic spines in the hippocampal CA1 region.     

Attribution of human infections with Shiga toxin‐producing Escherichia coli (STEC) to livestock sources and identification of source‐specific risk factors,The Netherlands (2010–2014)

Shiga toxin‐producing Escherichia coli (STEC) is a zoonotic pathogen of public health concern whose sources and transmission routes are difficult to trace. Using a combined source attribution and case–control analysis, we determined the relative contributions of four putative livestock sources (cattle, small ruminants, pigs, poultry) to human STEC infections and their associated dietary, animal contact, temporal and socio‐econo‐demographic risk factors in the Netherlands in 2010/2011–2014. Dutch source data were supplemented with those from other European countries with similar STEC epidemiology. Human STEC infections were attributed to sources using both the modified Dutch model (mDM) and the modified Hald model (mHM) supplied with the same O‐serotyping data. Cattle accounted for 48.6% (mDM) and 53.1% (mHM) of the 1,183 human cases attributed, followed by small ruminants (mDM: 23.5%; mHM: 25.4%), pigs (mDM: 12.5%; mHM: 5.7%) and poultry (mDM: 2.7%; mHM: 3.1%), whereas the sources of the remaining 12.8% of cases could not be attributed. Of the top five O‐serotypes infecting humans, O157, O26, O91 and O103 were mainly attributed to cattle (61%–75%) and O146 to small ruminants (71%–77%). Significant risk factors for human STEC infection as a whole were the consumption of beef, raw/undercooked meat or cured meat/cold cuts. For cattle‐attributed STEC infections, specific risk factors were consuming raw meat spreads and beef. Consuming raw/undercooked or minced meat were risk factors for STEC infections attributed to small ruminants. For STEC infections attributed to pigs, only consuming raw/undercooked meat was significant. Consuming minced meat, raw/undercooked meat or cured meat/cold cuts were associated with poultry‐attributed STEC infections. Consuming raw vegetables was protective for all STEC infections. We concluded that domestic ruminants account for approximately three‐quarters of reported human STEC infections, whereas pigs and poultry play a minor role and that risk factors for human STEC infection vary according to the attributed source.     

Ammonia dynamics in relation to hatching in Atlantic halibut (Hippoglossus hippoglossus L.)

Total ammonia content (T_Amm) and excretion (J_Amm), and ionic content (K⁺, Na⁺, Cl_-) have been studied in embryos and yolk-sac larvae of Atlantic halibut (Hippoglossus hippoglossus L.) maintained in darkness (6 °C and 34% S) or in light (light-arrested, nonon-hatching embryos). The T_Amm of the eggs increased from 250-300 nmol ind^-1 during the first 5-10 days post fertilization (dPF) to 400-500 nmol ind^-1 at the time of natural hatching in darkness. T_Amm did not start to decrease before 2-5 days after hatch, and yolk-sac larvae had a higher T_Amm compared to the light-arrested embryos of the same age and batch. J_Amm increased exponentially rom about 0.05 nmol ind^-1 h^-1 at 10 dPF to about 3 nmol ind^-1 h^-1 at hatch. Embryos undergoing hatching showed a significantly higher J_Amm than non-hatching, light-arrested embryos of the same age. The content of K+ in distilled water rinsed eggs declined from about 0.85 µmol ind^-1 at 2-4 dPF to about 0.15 µmol ind^-1 at hatch, while that of Cl^- remained constant at about t 0.85 µmol in^-1, and that of Na⁺ increased slowly from 0.10 to 0.20 µmol ind^-1 . Based on the measured ions, there was an anionic deficit in the egg, especially during the first week of development. When exposed to increased ambient total ammonia (0-27 mM NH4Cl), no mortality occurred, and no significant increase was found in the T_Amm of the Atlantic halibut egg before 9.2 dPF despite an estimated large inward diffusion gradient for the un-ionized ammonia species (NH₃). The delayed release of T_Amm comp ared to embryos and yolk-sac larvae of other marine teleosts, may relate to the deep-water spawning of the Atlantic halibut, and the buoyancy regulation of the yolk-sac larvae.     

氨氮胁迫对中国明对虾血淋巴氨氮、尿素氮含量和抗氧化能力的影响

将600尾体重为(5.0±1.2)g的健康中国明对虾(Fenneropenaeus chinensis)随机分为5组,每组6个重复,每个重复20尾虾,分别暴露于不同氨氮质量浓度(0 mg/L、2 mg/L、4 mg/L、6 mg/L和8 mg/L)海水中,于胁迫后6 h、24 h、48 h、72 h和96 h测定血淋巴氨氮、尿素氮含量、总抗氧化能力(T-AOC)、抗超氧阴离子活力和血淋巴细胞过氧化氢酶(CAT)基因、过氧化物还原酶(Prx)基因和含半胱氨酸的天冬氨酸蛋白水解酶(caspase)基因的相对表达量,以0 mg/L氨氮组作为对照。结果显示,随着氨氮胁迫时间的延长,中国明对虾血淋巴氨氮含量逐渐积累,以8 mg/L组对虾血淋巴氨氮含量最高,是对照组的5.85倍。氨氮胁迫6 h,胁迫组中国明对虾血淋巴尿素氮含量显著高于对照组(P0.05),其中6 mg/L组对虾血淋巴尿素氮含量最高,是对照组的2.22倍。氨氮胁迫下中国明对虾血淋巴T-AOC、Prx mRNA相对表达量随着取样时间推移先升高后降低,而血淋巴抗超氧阴离子活力、CAT和caspase mRNA相对表达量随时间增加呈现先上升后下降再上升的变化过程。氨氮胁迫下中国明对虾血淋巴抗氧化能力被显著诱导,这可能破坏机体的氧化-抗氧化系统的平衡,从而导致caspase mRNA相对表达量的上调。     

Marine protected areas and ocean basin management

1. All reserve designs must be guided by an understanding of natural history and habitat variability. 2. Differences in scale and predictability set aside highly dynamic pelagic systems from terrestrial and nearshore ecosystems, where wildlife reserves were first implemented. Yet, as in static systems, many pelagic species use predictable habitats to breed and forage. Marine protected areas (MPAs) could be designed to protect these foraging and breeding aggregations. 3. Understanding the physical mechanisms that influence the formation and persistence of these aggregations is essential in order to define and implement pelagic protected areas. We classify pelagic habitats according to their dynamics and predictability into three categories: static, persistent and ephemeral features. 4. While traditional designs are effective in static habitats, many important pelagic habitats are neither fixed nor predictable. Thus, pelagic protected areas will require dynamic boundaries and extensive buffers. 5. In addition, the protection of far‐ranging pelagic vertebrates will require dynamic MPAs defined by the extent and location of large‐scale oceanographic features. 6. Recent technological advances and our ability to implement large‐scale conservation actions will facilitate the implementation of pelagic protected areas. 7. The establishment of pelagic MPAs should include enforcement, research and monitoring programmes to evaluate design effectiveness. 8. Ultimately, society will need a holistic management scheme for entire ocean basins. Such overarching management will rely on many innovative tools, including the judicious use of pelagic MPAs. Copyright © 2000 John Wiley & Sons, Ltd.     

The impact of phenology,exposure and instar susceptibility on insecticide effects on a chrysomelid beetle population

Direct topical impact of an insecticide spray on a population of a non-target leaf-eating beetle, Gastrophysa polygoni, was studied, and the relative importance of phenology, instar susceptibility and instar specific exposure was evaluated. Two insecticides, cypermethrin and dimethoate, were investigated. In the laboratory, topical toxicity to eggs, second-instar larvae and adults was recorded in dose-response experiments. The spatial distribution of larvae and eggs were measured in the field. Deposition of insecticide onto eggs, second-instar larvae and adult specimens was measured at different positions within the crop canopy by use of a dye tracer technique. A temperature-driven population model was constructed to simulate population development of all life stages in the field. The model was based on laboratory measures of growth and development at various temperatures. Mortality due to direct insecticide exposure was calculated as a function of population demography, spatial distribution of individuals, spatial deposition of the insecticide, and stage-specific susceptibility. Cypermethrin had the greatest impact, reducing population size by 19–32%. The life stages most sensitive to cypermethrin were the larval instars. As the population developed from eggs to larvae and imagines, the impact of one spraying first increased and then decreased according to the proportion of larvae in the population. Dimethoate had less effect on the population, i.e. 1·9–7·6% reduction. Dimethoate was most toxic to the egg stage, and consequently the effect on the population decreased as the proportion of eggs decreased due to hatching. The direct effect of insecticide spraying was significantly affected by all three factors investigated, i.e. phenology, life stage susceptibility and stage-specific exposure. The latter factor is composed of both spray flux at various spatial positions in the canopy and the ability of different life stages to retain spray droplets. © 1998 SCI     

Tolerance of Atlantic salmon (Salmo salar) to dietborne endosulfan assessed by haematology,biochemistry, histology and growth

The inclusion of plant‐based ingredients in commercial fish feeds may pose a challenge because of the presence of undesirable substances, such as the pesticide endosulfan. Waterborne endosulfan is highly toxic to fish, whereas dietborne exposure has varied toxicity in different species. To investigate the systemic effects of endosulfan exposure, quadruplicate groups of Atlantic salmon (Salmo salar) were fed either 0 (control), 0.005 mg kg^?1; the European Union's maximum limit, or 10 or 20 times this level (0.05 and 0.1 mg kg^?1 respectively) for 95 days. There were no significant differences (P > 0.05) in liver somatic index, spleen somatic index, condition factor or growth among treatments. There were no indications of liver damage in fish from any of the groups in the biomarkers measured: plasma aspartate aminotransferase, plasma alanine aminotransferase and histopathology. Similarly, there were no apparent treatment‐related effects on the haematological parameters Hct, Hb, mean corpuscular volume, mean corpuscular haemoglobin concentration and mean corpuscular haemoglobin, and blood sodium, potassium, calcium and chloride levels were not significantly (P > 0.05) different among groups. Lipid digestibility, but not energy, protein, or glycogen digestibility, was significantly (P < 0.05) reduced at the highest exposure concentration. However, no significant differences were observed in lipid production value or lipid efficiency ratio. In contrast to previous studies, clinical histological abnormalities were not observed in the intestine, liver or spleen of endosulfan‐treated fish.     

Dietary α‐Ketoglutarate supplementation alleviates harmful effects of high environmental ammonia on grass carp,Ctenopharyngodon idella

Current intensive fish farming usually causes high environmental ammonia (HEA) in ponds that is toxic to fish. α‐Ketoglutarate (α‐KG) can be rapidly transaminated to glutamic acid and further aminated to glutamine. Therefore, we hypothesized that dietary α‐KG supplementation would alleviate HEA toxicity to fish. To test the hypothesis, 270 healthy grass carp (Ctenopharyngodon idella) juveniles were randomly assigned to control, HEA (18.37 mg/L ammonia) and HEA + α‐KG (0.75% of α‐KG) groups. Ammonia and free amino acid content in plasma and brain, liver glutamic pyruvic transaminase and glutamic oxaloacetic transaminase activity, and urea and glycogen content were measured on the first, seventh and 42nd days. Our results showed short‐term HEA exposure (1 day) led to a significant ammonia accumulation in the brain and plasma and significantly decreased glutamic and aspartic acid content in the brain and increased glutamine content in the brain and plasma. The long‐term HEA exposure (42 days) caused significant reductions in glycine and arginine content in the brain tissue. In most cases, dietary α‐KG supplementation alleviated the fluctuations in FAA content in the brain and plasma. Our results suggested dietary α‐KG alleviated HEA toxicity to grass carp.