China ; Dust ; analysis ; Female ; Humans ; Male ; Manufactured Materials ; Occupational Exposure ; prevention & control ; statistics & numerical data ; Occupational Health

Objective To know the condition and feature of water-born endemic arsenism in Shaanxi province, and to provide scientific evidences for prevention and treatment of the disease. Methods In 2009, 8 villages of Duhe, Miaogou, Sanhe, Caiyuan in Shanyang county and Shuanglong, Guangming, Donghekou in Zhen'an county and Guojiawan in Mian county as monitoring sites from both the found water-born arsenic poisoning areas and potential ones of drinking water arsenic ＞ 0.15 mg/L were selected. The disease conditions of residents who lived for more than six months of continuous residence, were investigated according to "Endemic Arsenism Diagnostic Criteria" (WS/T 211-2001 ) and arsenic level in the drinking water were determined. Results Seven thousand six hundred and ninety-three individuals were investigated and 612 cases of arsenism were diagnosed in the 8 villages, the prevalence rate was 7.96%(612/7693). Mild patients accounted for 33.17%(203/612), moderate patients accounted for 50.16%(307/612), and severe patients accounted for 16.67%(102/612). The detection rate for male was 9.99%(408/4085), for female was 5.65%(204/3608), the former was higher than the latter(x2 = 49.138,P ＜ 0.01 ). The older the age was, the higher the rate was(x2 = 770.708, P ＜ 0.01 ). Main clinical manifestation of the patients was depigmentation and pigmentation in skin. Patients with one symptom accounted for 43.30% (265/612), with two symptoms accounted for 56.70% (347/612). Three hundred and seventy drinking water samples were detected, the median of arsenism content was 0.005 mg/L, ranged 0 - 1.660 mg/L. The over-limit rate of arsenic level in the drinking water were 11.62% (43/370). Conclusion Water-born endemic arsenism is mildly prevailing in Shaanxi province, however, great attention should be given to control and monitoring of the disease.

Objective To investigate the current situation of endemic fluorosis associated with drinking water in Shaanxi province in 2008, providing prevention and control work with scientific evidence. Methods According to data of drinking water endemic fluorosis in Shaanxi, 15 counties in Yulin, Weinan and Xianyang city were divided into mild, moderate and severe diseased areas according to fuoride level in the drinking water or the fluorosis severity, and 12,39,45 endemic fluorosis villages were selected respectively from each area. Dental fluorosis for all the children aged 8 - 12 years old and clinical skeletal fluorosis for the people over the age of 16 were examined. In mild, moderate and severe areas, 30% of the survey villages received X-ray to examine skeletal fuorosis. Five water samples were collected from villages with unimproved water respectively from the east, the west, the south, the north, the middle; if there was less than 5 that could be sampled, then all were collected, moreover 3 peripheral and 1 central water samples were collected from villages with improved water. Also in mild, moderate and severe illness areas, 50% of the surveyed villages were selected; in each village, 30 urine samples of the children aged 8 - 12 were collected, 6 portions in each age group. If Less than 30 children in all the age groups or less than 6 in each age group, all their urine samples were collected to determine fluoride. Results Totally 3652 children aged 8 - 12 years old were examined and 1930 cases of dental fluorosis were diagnosed, the rate was 52.85% and the index was 1.22. The rates in Dinghian, Jingbian and Pucheng village were higher, being 90.43% (170/188) ,82.89%(126/152),80.65% (325/403) respectively. A total of 40 543 adults over the age of 16 were examined and 5935 cases of skeletal fluorosis were diagnosed, in a rate of 14.64%. The rates of the mild, moderate, severe skeletal fluorosis were respectively 9.17%(3717/40 543),4.36%(1769/40 543),1.11%(449/40 543).All 706 adults were taken X-ray films.and 280 cases of positive change were diagnosed,the positive rate was 39.66%. The rates of the mild,moderate,severe change were respectively 17.28%(122/706),17.00%(120/706),5.38%(38/706).All 427 water samples were collected,the fluoride content waS(2.22±1.41)ms/L,and the abnormal rate was 85.01%(363/427).All 1393 portions of urine sample were collected in children and the median of fuoride was 2.37 mg/L Conclusions The endemic fluorosis associated with drinking water is still comparatively serious in Shaanxi.The preventive measures for improving water must be improved.

The research status is reviewed on taxonomic position, ecology, biological active matter and artificial cultivation of Shiraia bambusicola. Following problems are presented: whether there are new species and host specificity of Shiraia bambusicola. Since the artificial cultivation of stroma of Shiraia bambusicola has not been success, Shiraia bambusicola is in situation of emerge of itself and perish of itself so that it is not beneficial to resource protection and continual utilization of this medicinal fungus. It is pointed out that molecular biology of Shiraia bambusicola should be further researched and technology of artificial cultivation of Shiraia bambusicola should be explored in order to exploit and usage of Shiraia bambusicola.

Objective To investigate the status of the disease of the fluorosis and arsenism caused by coal-burning in Ankang city of Shaanxi. Methods Nine survey spots were chosen to carry out the epidemiological investigation of adult skeletal fluorosis and arsenism in the coal-polluted areas of Ankang, respectively using Determination of Fluorine in Coal (GB/T 4633-1997) to determine the coal fluorine and using hydride generation atomic fluorescence spectrophotometry(HCAFS) to determine coal arsenic. The diagnose of the adult skeletal fluorosis followed the Diagnosis of Clinical Classification for Endemic Skeletal Fluorosis Standard(GB 16396-1996), that of arsenism using Standard of Diagnosis for Endemic Arsensim (WS/T 211-2001). Results Totally 569 adults were investigated over the age of 16, among which 121 cases were skeletal fluorosis, with a total detection rate of 21.27%. Four cases of II degree and higher skeletal fluorosis patients were identified, accounting for 0.70% of the number of subjects. One hundred and thirty-two cases of arsenic poisonin were detected, in a rate of 23.20%. Ninety-five patients were identified with moderate or severe arsenic poisoning, accounting for 16.69% of subjects. A positive correlation was found between the detection rates of the skeletal fluorosis and the arsenism(r = 0.816, P < 0.01), as well as between the detection rate of skeletal fluorosis and fluoride content of coal(r = 0.775, P < 0.05). The detection rate of arsenism and arsenic content of coal also had close relationship (r = 0.761, P < 0.05). The detection rate of skeletal fluorosis in the group aged 40 - ,50 - , and 60 - [27.20%(34/125) ,29.27%(36/123), 28.13%(36/128)] was increased, compared the group of less than 40 years age[7.77%( 15/193), X~2 = 21.969,25.648,23.856,P<0.01].For the detection rate of arsenism,male[33.67%(99/294)]was obviously higher than female[12.00%(33/275),)(X~2=37.162,P<0.01].Conclusions A high detection rate of fhorosis is correlated with arsenic poisoning,but the probability of the two diseases simultaneously occurred in a person is not high.In this polluted area.when fluoride accumulates to a certain level as in aduh,the detection rates no longer varies obviously;however,that of arsenism increases along with the age.

ObjectiveTo investigate the current situation of coal-burning borne endemic fluorosis in the infected area,the usage of defluoridation stove and the formation of related behavior; to evaluate the control effect,so as to provide a theoretical basis for superiors' policy-making.MethodsNine villages in three counties of Ankang city and Hanzhong city Shanxi province were monitored in 2010.Choose five disease infected villages with oven changed in the three monitoring counties,and 10 families were randomly selected in each of the nine monitoring points and every chosen village,and a survey on the stove using and related behavior changes was carried out.By using Dean method,the dental fluorosis of every child aged 8 - 12 in the monitoring villages was examined.Meanwhile 10 copies of urine samples were randomly collected in each age group in the above-mentioned villages.The content of fluoride in urine was determined by F-ion selective electrode(WS/T 30-1996) and evaluated according to “The Normal Concentration of Urinary Fluoride of Population” (WS/T 256-2005).Twenty men over 25years old in the monitoring counties were randomly selected in each age group to be examined skeletal fluorosis by X-rays,and diagnosis was based on “The Endemic Skeletal Fluorosis Standard”(WS 192-2007).ResultsThe proper utilization rate and the qualified households of iron stoves and improved stoves,the correct drying rate and the correct storage rate of peppers and coms were all low.The washing rate of corns and peppers before eating was higher than 95％.Of the 350 children being examined of dental fluorosis in the 9 monitoring villages,the detection rate of dental fluorosis was 59.71％ (209/350).A total of 871 adults over the age of 25 were examined,and the detection rate of skeletal fluorosis was 17.22％ (150/871).A total of 350 copies of children urine samples were tested and the fluoride content were between 0.07 - 2.02 mg/L,the geometric mean value of fluoride content was 0.66 mg/L.ConclusionsThe coal-burning borne endemic fluorosis in Shanxi is in a growth phase,many defluoridation stoves are out of order,and the formation of healthy behaviors is low.To strengthen the disease surveillance,health education and management of defluoridation stoves are keys to prevent coal-burning borne endemic fluorosis in the future.

Objective To investigate the running conditions of the water improvement projects and the role of these projects in reducing fluoride in drinking-water type of fluorosis in Shaanxi province, and provide a scientific basis for prevention and control of the disease. Methods Forty-eight villages of 16 counties in Xi'an, Baoji, and Yulin cities of Shaanxi province were monitored in 2009. Five water samples were collected randomly in water unimproved monitoring villages by the position of east, west, south, north, and center parts. In water improved monitoring villages, 3 tap water and one source water samples were collected. Water fluoride was tested using fluoride ion selective electrode method according to the "Standard Testing Methods for Drinking Water" (GB/T 5750-2006). All school children aged 8 to 12 in monitored villages were examined their dental fluorosis using Dean criteria. All people over 16 years old were examined clinical skeletal fluorosis, and 30% of the project counties were randomly selected, then randomly selected one village among these counties, clinically diagnosed patients with skeletal fluorosis were examined again by X-ray using "Diagnostic Criteria of Endemic Skeletal Fluorosis"(WS 192-2007). Urine samples of 30 children aged 8 to 12 and of 20 adults over the age of 16 were randomly collected, urinary fluoride was tested according to "the Determination of Urinary Fluoride by Ion Selective Electrode Method" (WS/T 89-19%). Results Of the 22 water improvement projects that in normal operation, fluoride level of 8 source waters exceeded the standard, accounting for 36.36%(8/22), and projects scrapped 5. Two hundred and two water samples were tested. In water improved historical diseased areas, the median of water fluoride of source water and tap water were 0.72,0.62 mg/L, respectively, and the average rate of water fluoride exceeded the standard ere 36.36%(8/22) and 31.94%(23/72), respectively. In water unimproved historical diseased areas, the median of water fluoride was 1.00 mg/L, and the average rate of water fluoride exceeded the standard was 39.81%(43/108). Detection rate of dental fluorosis among children aged 8 to 12 was 16.06% (367/2285), dental fluorosis index was 0.30, and the prevalence was negative. Detection rate of clinical skeletal fluorosis among adults over 16 years old was 5.09%(1542/30 272), a totally of 198 people had X-ray film taken, positive 68, the positive detection rate was 34.34%(68/198). One thousand and fifty-one copies of children's urine samples were tested, geometric mean of urinary fluoride was 0.95 mg/L; nine hundred and fourteen copies of adults urine samples were tested, geometric mean of urinary fluoride was 1.16 mg/L Conclusions Drinking-water type of fluorosis affects a large area in Shaanxi province, the disease is still serious, and the task of prevention remains very arduous. Further intensify the water improvement project in diseased areas, and strengthen disease monitoring, health education and water improvement project management is the key to prevention and control of endemic fluorosis.

Poly(ADP-ribose) polymerase-1 (PARP-1) has emerged as a promising anticancer drug target due to its key role in the DNA repair process. It can polymerize ADP-ribose units on its substrate proteins which are involved in the regulation of DNA repair. In this work, a novel series of para-substituted 1-benzyl-quinazoline-2, 4 (1H, 3H)-diones was designed and synthesized, and the inhibitory activities against PARP-1 of compounds 7a-7e, 8a-8f, 9a-9c and 10a-10c were evaluated. Of all the tested compounds, nine compounds displayed inhibitory activities with IC50 values ranging from 4.6 to 39.2 micromol x L(-1). In order to predict the binding modes of the potent molecules, molecular docking was performed using CDOCKER algorithm, and that will facilitate to further develop more potent PARP-1 inhibitors with a quinazolinedione scaffold.
Antineoplastic Agents ; chemical synthesis ; chemistry ; pharmacology ; Drug Design ; Enzyme Inhibitors ; chemical synthesis ; chemistry ; pharmacology ; Molecular Docking Simulation ; Molecular Structure ; Poly (ADP-Ribose) Polymerase-1 ; Poly(ADP-ribose) Polymerases ; Quinazolinones ; chemical synthesis ; chemistry ; pharmacology ; Structure-Activity Relationship

Objective To evaluate the application value of X-ray,echocardiogram,pulmonary perfusion scintigraphy,EBCT,Magnetic resonance Pulmonary angiography in diagnosis of PTE.Methods Twenty-five consecutive patients clinically diagnosed of having PTE were examined from july 2003 through March 2004. Patients underwent X-ray chest plain film, echoeardiogram, electronic beam computed tomographie (EBCT)angiography,ventilation-perfusion (V-P)seintigraphy,Magnetic resonance Pulmonary angiography (MRPA)and puhnonary angiography according to a strict diagnostic protocol.Two of the independent readers reviewed the pulmonary angiography and record all of the lobe and segmental involved in PTE and compared with other image method.Results Pulmonary angiography:all of the patients success underwent the technique,the pulmonary artery branch with PTE was in 556 of 775 branches (71.7%). Chest radiography had hints of diagnosis in 12 of 25 patients.Nine patients diagnosed with echocardiogram. Right heart enlargement was in 21,and pulmonary hypertension in 18.V-P scintigraphy revealed 247 segmental involved with PTE of 500 (52.0% ),and the sensitivity was 64.66% compare with the pulmonary angiography.There were 523 pulmonary branches involved PTE with EBCT pulmonary angiograpy of 775 branches,and the sensitivity was 94.06%.MRPA: 8 of 10 patients succeed in the technique, 155 branches of 248 were detected with PTE(62.5% ),the sensitivity was 81.29%.Conclusions EBCT is a high sensitivity method in diagnosis of PTE.Chest radiography and echocardiogram are the first-line modality of PTE.V-P scintigrapby is the valid compensation in diagnosis subsegmental pulmonary artery with PTE when EBCT miss diagnosis.Gd-CE-MRPA may be the second-line modality in diagnosis of PTE.

Objective To dynamically investigate the effects of aluminum on the concentration of free intracellular Ca2+([Ca2+]i) and the expression of calcium channels in the hippocampus of rats. Methods Healthy 64 Wistar rats were taken as the experimental objects. And these rats were randomly divided into 16 groups according to their weights, and were instilled with AlCl3 at 0(control),37.3,74.7 and 248.7 mg/kg respectively. The experimental time exposed to AlCl3 was 45,75,120 d, among which the rats were given AlCl3 for 120 d fed normally for 30 d. The hippoeampus were segregated on day 45,75,120 and 150 d and the[Ca2+]i of hippocampus of rats were detected by fluorospectrophotometer. The expression of Ryanodine receptor 2 (RyR2) mRNA and α1C ubunit of L-type calcium ehannels(L-Ca2+α1C) mRNA were detected by RT-PCR analysis. Results [Ca2+]i was increased by AlCl3 in a dose-and time-dependant manner(F=23.136 and 19.089, P<0.01). There was a synergistic effect between the dose and time in [Ca2+]i (F=2.270, P<0.05). In time of 120,150 days, the [Ca2+]i of rats hippocampus in 37.3[(299.3±48.7), (342.7±35.3)nmol/L], 74.7[(391.2±47.9), (408.1±42.8)nmol/L] and 248.7 mg/kg group[(397.9±55.8), (405.2±22.7)nmol/L] significantly increased compared with control group [(195.1±29.9), (209.1±30.6)nmol/L; P<0.01]. The expression of RyR2 mRNA and L-Ca2+α1C mRNA were increased by AlCl3(F=23.301 and 60.812, P<0.01). The experimental time could lower the expression of L-Ca2+ α1C mRNA (F=6.088, P<0.01), but had no influences on the expression of RyR2 mR NA (F=1.361, P>0.05). There was interaction between the dose of AlCl3 and the time in the expression of L-Ca2+α1C mRNA (F=5.876,P< 0.01). On day 75,120 and 150 of the experiment, the expression of L-Ca2+α1C mRNA in rat hippocampus of 74.7 (1.03±0.16,1.18±0.18,0.92±0.11) and 248.7 mg/kg group(1.89±0.26, 1.25±0.10, 1.07±0.14) also increased compared with control group(0.63±0.09,0.78±0.16,0.69±0.11; P<0.05 or <0.01). On day 45,75, 120 and 150 of the experiment, the expression of RyR2 mRNA in 74.7(0.49±0.06,0.51±0.07,0.57±0.11, 0.47±0.11), 248.7(0.47±0.03,0.52±0.09, 0.70±0.10, 0.78±0.09)mg/kg AlCl3 groups was highly increased compared with control group (0.24±0.07, 0.32±0.04, 0.30±0.06, 0.27±0.06; P<0.05 or<0.01). Conclusion Al increases [Ca2+]i by increasing the expression of the RyR2 mRNA and L-Ca2+α1C mRNA, thus exerts an irreversible neuronal toxicity.