Objective To investigate the relationship between herpes simplex virus(HSV) and spontaneous abortion. Methods 40 aborted material and 16 post-aborted curettings were tested for the presence of HSVDNA with in situ hybridization.In addition 20 normal endometria and 20 induced abortive placentas were used as controls. Results 56.3 %(9/16)post-abortion curettings were demonstrated the presence of HSVDNA.It was higher than that of the control group( P

Objective To improve the diagnosis and treatment of primary adrenocortical carcinoma. Methods Retrospective analysis was performed in clinical data of 16 patients with primary adrenocortical carcinoma. The diagnosis was based on clinical presentations,hormonal studies and imaging. Surgical treatment was underwent on 13 cases. All patients were followed up for 3 to 62 months. Results Of 16 cases,functional tumors were in 8,including Cushing′s syndrome in 5,combination of Cushing′s syndrome and virilization in 2,and hyperaldosteronism in 1. Imaging studies revealed the tumors were 4.8 to 19.5 cm in diameter,average in 7.8 cm. Distant metastasis occurred in 3 cases. Radical surgery was done in 13 cases without distant metastasis,including radical adrenalectomy in 8,adrenalectomy plus nephrectomy in 2,adrenalectomy plus surgical extirpation of intracaval tumor thrombus in 2,and partial resection of the wall of inferior vena cava in 1. Pathologic stages were stage Ⅰ in 2 cases,stage Ⅱ in 8,stage Ⅲ in 3,stage Ⅳ in 3. Among the 11 cases who were treated over 2 years after operation,6 cases were still survival,while 1 case had pulmonary and 1 case had bone metastasis. The other 5 cases survive in average of 26 months. Conclusions Prognosis of primary adrenocortical carcinoma is poor. The keys to early diagnosis are clinical manifestations plus imaging. Surgical treatment is the only effective therapy for the disease.

Objective To investigate the association of bacterial translocation (BT) with cachexia in colonic cancer patients.Methods From September 2015 to May 2017 the clinical data of 292 colon cancer patients were studied at Qingdao Municipal Hospital.The bacteria in peripheral blood and mesenteric lymph nodes were detected by bacterial culture,and the bacterial DNA in peripheral blood was detected by PCR technique to determine the occurrence of bacterial translocation.Intestinal epithelial T-cell subsets and NK cells were evaluated using flow cytometry.Western blot and immunofluorescence were used to check tight junction proteins Occludin,Claudins-2,Zonula occluden-2 in intestinal epithelium.Fluorescence in situ hybridization and immunohistochemistry were used to detect the translocated bacteria and endotoxin.Results Compared with noncachectic patients,cachectic patients had a significandy higher BT ratio (27.8％ vs.7.2％,x2 =20.871,P ＜ 0.001).BT in the intestinal mucus layer was associated with lower levels of T-cell subsets and NK cells in the intestinal epithelium in BT(+) patients (CD3 + T:36.69％ ±5.87％ vs.41.63％ ±5.03％,CD4+T:44.08％ ±5.12％ vs.49.58％ ±7.01％,CD8+T:65.68％ ±5.51％ vs.61.43％ ± 5.58％,CD4+ T/CD8+ T:0.71％ ± 0.21％ vs.0.91％ ±0.23％,NK:27.86％ ± 3.93％ vs.34.69％ ± 4.52％,all P ＜ 0.01).Endotoxin was detected within the small intestinal wall in BT(+) patients and claudin-2 expression increased (0.63 ± 0.13 vs.0.21-± 0.06,t =-2.936,P ＜ 0.01),whereas Occludin and Zonula occluden-2 expressions decreased (0.37 ± 0.13 vs.0.84±0.17,0.16±0.07 vs.0.58±0.19,t=2.151,2.111,bothP＜0.05).Conclusions BTmay contribute to the development of colon cancer cacheria,and tight junction could be the gateway of BT.

Objective: To understand the cognitive and management status of breast cancer patients with expectant nausea and vomiting in breast cancer patients, and to provide reference for taking targeted measures to improve the symptoms of nausea and vomiting. Methods: From March to May 2018, 10 breast surgical nurses were selected by the purpose sampling method. The phenomenological research methods in qualitative research were used to interview them. The Colaizzi data analysis principle was used to analyze the data and refine the theme. Results: A total of five themes were extracted: nurses generally knew the impact of nausea and vomiting on patients; lack of knowledge about the expected nausea and vomiting of chemotherapy; nausea and vomiting has not been evaluated as an independent symptom; there is still no targeted, systematic management Measures; lack of attention is a major obstacle to the management of nausea and vomiting in patients. Conclusion Nurses should strengthen the knowledge of chemotherapy-predicted nausea and vomiting in breast cancer patients, and effectively evaluate patients with nausea and vomiting. Nursing managers should formulate corresponding standardized interventions to improve patients' nausea and vomiting according to the existing problems. Improve the quality of life of patients.

Objective: To evaluate the effects of continued acceptance and commitment therapy intervention on post-traumatic growth of postoperative patients with breast cancer. Methods: According to the hospitalization time, 120 patients with breast cancer were divided into observation group (62 cases) and control group (58 cases). From January to December 2017, 58 patients were used as control group. Regular health education and discharge follow-up were performed. Intervention with the commitment therapy 3 times; 62 patients from January to December 2018 were selected as the observation group. On the basis of the control group, the patient continued to receive and commit the intervention for 3 to 4 times from February to March after discharge. The post-traumatic growth status of patients before, at the time of discharge (after the intervention), at the hospital for 2 months, at the hospital for 3 months, and at the hospital for 6 months was assessed using the Simplified Chinese version of the Post-Treatment Growth Rating Scale (PTGI). Results: There was no significant difference in the post-traumatic growth scores between the two groups (P>0.05). The post-traumatic growth scores of the two groups were 67.02±14.17, 66.93±14.24, which were better than 51.72±11.65, 51.86±11.67 before the intervention (t= 7.634, 7.725, P<0.05). At 3 months and 6 months after discharge, the post-traumatic growth scores of the observation group were (67.12±14.07) and (68.21±14.48), which were significantly better than the control group (54.17±11.64). 54.02±11.12), the difference was statistically significant (t= 7.957, 7.674, P<0.01). Conclusion Acceptance and commitment therapy intervention during hospitalization can effectively improve post-traumatic growth of postoperative patients with breast cancer. Continued admission and commitment therapy intervention after discharge can provide patients with out-of-hospital continuous care programs to improve post-traumatic growth of postoperative patients with breast cancer. It has a better long-term effect than the control group.

Objective To investigate the effect of long?term exposure to environmental cadmium on eight mineral element's metabolic balance of human body. Methods To choose a high cadmium area polluted by smelting and mining north of Guangdong province and a cadmium?free area with a similar economic level, and living and eating habit of residents as a contrast from April 2011 to August 2012. Stratified random sampling and clustered sampling method were adopted to choose the non?occupationally cadmium?exposed respondents who have lived in local area for more than 15 years, older than 40 years, having local rice and vegetable as the main dietary source, with simple and relatively stable diet, and without diabetes, kidney disease, thyroid disease, liver disease or other history of chronic disease. This study included 298 respondents, of whom 155 were in cadmium exposure group and 143 in control group. Questionnaires was used to acquire their health status and their morning urine samples were collected. Electrolytically coupled plasma mass spectrometry (ICP?MS) was used to test the concentrations of sodium (Na), magnesium (Mg), phosphorus (P), potassium (K), calcium (Ca), copper (Cu), zinc (Zn) and iodine (I). The Mann?Whitney U test method was used to compare the differences of concentrations of urinary cadmium, Na, Mg, P, K, Ca, Cu, Zn, I, and the ratio of Na to K (Na/K), Ca to P (Ca/P) between exposed group and control group.χ2 test was used to compare the abnormal rate of urinary cadmium between exposed group and control group. Pearson correlation and multiple regression method were used to investigate the relationship between urinary cadmium levels, gender, age, smoking, passive smoking, and minerals. Results The urinary cadmium level P50 (P25-P75) in exposed group was 5.45 (2.62-10.68)μg/g·cr, which was higher than that of the control group, which was 1.69 (1.22-2.36)μg/g · cr (Z=-10.49, P<0.001). The abnormal rate of urinary cadmium was 51.6%(80/155), which was higher than that of the control group (2.8%(4/143)) (χ2=87.56,P<0.001). The urinary Ca, Cu, Zn, and I level P50 (P25-P75) of exposed group were 173.80 (114.40-251.70), 20.55 (14.95-28.44), 520.23 (390.25-647.15), and 246.94 (203.65-342.97)μg/g · cr, which were higher than those in control group (142.42 (96.87-179.11), 15.44 (12.26-20.98), 430.09 (309.85-568.78) and 213.85 (156.70-281.63) μg/g · cr, respectively) (Z values were-4.33,-5.04,-3.47 and-4.24, all P values<0.001). The urinary P, K level P50 (P25-P75) of exposed group were 582.50 (463.20-742.8), 890.10 (666.00-1 305.40) μg/g · cr, which were lower than control group (694.50 (546.20-851.17), 1 098.58 (904.53-1 479.18) μg/g · cr) (Z values were-3.36,-4.02, all P values <0.001). on Based the results of Pearson correlation analysis, urinary cadmium was positively correlated with urinary Ca, Cu, Zn, and I, and the correlation coefficients were 0.31, 0.61, 0.38, and 0.25, respectively(all P values<0.05). Based on the results of multiple regression analysis, urinary cadmium levels contributed most to the metabolic balance of urinary Ca, Cu, Zn and I. The standardized regression coefficients were 0.31, 0.59, 0.39, and 0.24, respectively (all P values<0.001). Conclusion Long?term environmental exposure to cadmium affected the metabolic balance of Ca, Cu, Zn and I in human body.

Objective To investigate dynamic change of cadmium body burden and renal dysfunction among residents living in cadmium?polluted areas. Methods From April to July of 2011, the cadmium?polluted areas of northern Guangdong province in China was chosen as the study site. Based on the levels of cadmium pollution in soil and rice, the survey areas were divided into low exposed group (average concentration of cadmium was 0.15-0.40 mg/kg, 0.5-1.0 mg/kg in rice and soil, respectively) and high exposed group (average concentration of cadmium was >0.40 mg/kg, >1.0 mg/kg in rice and soil, respectively). Stratified random sampling and cluster sampling method of epidemiological investigations were carried out among 414 local residents who lived in cadmium exposure areas for more than 15 years, aged above 40, and without occupational cadmium exposure, including 168 and 246 residents in low and high exposed group, respectively. From March to June of 2014, 305 respondents of those who participated in 2011 were successfully traced, including 116 and 189 respondents in low and high exposed group, respectively. We used health questionnaires to acquire their health status. Home?harvested rice and vegetable samples were collected using quartering method for detection of cadmium level, including 190 rice samples, 161 vegetable samples in 2011 and 190 rice samples, 153 vegetable samples in 2014. Urine specimens of residents were collected for the detection of urinary cadmium and creatinine as well as renal dysfunction biomarkers, namely, N?acetyl?beta?D?glucosamidase (NAG) andβ2?microglobulin (β2?MG), respectively. In 2011 and 2014, Chi?square test was used to investigate the differences of abnormality of cadmium concentration in rice, vegetables and urinary cadmium,β2?MG,and NAG that were expressed as odds ratio (OR) and 95%confidence intervals (95%CI). Results In 2011 and 2014, cadmium concentration P50 (P25-P75) in rice was 0.43 (0.17-1.10) mg/kg,and 0.42 (0.20-1.14) mg/kg, respectively (Z=-0.77, P=0.440). In 2011 and 2014, cadmium concentrations P50 (P25-P75) in vegetables were 0.13 (0.07-0.34) mg/kg,and 0.25 (0.12-0.59) mg/kg, respectively, with abnormal rates of 38.5%(62/161) and 60.8%(93/153), respectively. In 2014, both average concentration and abnormal rate of cadmium in vegetables were higher than those in 2011 (Z=-4.69,P<0.001 andχ2=15.58, P<0.001). Concentrations of urinary cadmium P50 (P25-P75) in high exposed group were 7.90 (3.96-14.91)μg/g creatinine, 8.64 (4.56-17.60)μg/g creatinine in 2011 and 2014, respectively. Contrary to that in 2011, urinary cadmium of high exposed group was significantly increased in 2014 (Z=-2.80 ,P=0.005). In 2011 and 2014, concentrations of β2?MG, NAG P50 (P25-P75) were 0.15 (0.07-0.29)μg/g creatinine, 0.15 (0.07-0.45)μg/g creatinine,and 7.12 (5.05-10.65) U/g creatinine, 13.55 (9.1-19.84) U/g creatinine, respectively, with abnormal rates of 7.5% (23/305), 15.1% (46/305) ,8.2%(25/305) , and 33.8% (103/305), respectively. Compared with baseline in 2011, average concentrations ofβ2?MG, NAG significantly increased in 2014 (Z=-2.263,P=0.024 and Z=-12.52,P<0.001), and abnormal rates ofβ2?MG, NAG were also higher in 2014 (χ2=15.61,P<0.001 andχ2=64.72,P<0.001), with odds ratio (OR) of 2.00 (95%CI:1.23-3.24) and 4.12 (95%CI:2.87-5.92). Conclusion Environmental cadmium pollution of crops such as rice and vegetables in survey areas continued to remain high. Body burden of cadmium might kept at sustainably high levels and renal dysfunction was worsened after continuous, long?term cadmium exposure. Our results suggested that NAG might be more sensitive than β2?MG to serve as an indicator for an individual's future tubular function.

Objective To investigate the effect of long?term exposure to environmental cadmium on eight mineral element's metabolic balance of human body. Methods To choose a high cadmium area polluted by smelting and mining north of Guangdong province and a cadmium?free area with a similar economic level, and living and eating habit of residents as a contrast from April 2011 to August 2012. Stratified random sampling and clustered sampling method were adopted to choose the non?occupationally cadmium?exposed respondents who have lived in local area for more than 15 years, older than 40 years, having local rice and vegetable as the main dietary source, with simple and relatively stable diet, and without diabetes, kidney disease, thyroid disease, liver disease or other history of chronic disease. This study included 298 respondents, of whom 155 were in cadmium exposure group and 143 in control group. Questionnaires was used to acquire their health status and their morning urine samples were collected. Electrolytically coupled plasma mass spectrometry (ICP?MS) was used to test the concentrations of sodium (Na), magnesium (Mg), phosphorus (P), potassium (K), calcium (Ca), copper (Cu), zinc (Zn) and iodine (I). The Mann?Whitney U test method was used to compare the differences of concentrations of urinary cadmium, Na, Mg, P, K, Ca, Cu, Zn, I, and the ratio of Na to K (Na/K), Ca to P (Ca/P) between exposed group and control group.χ2 test was used to compare the abnormal rate of urinary cadmium between exposed group and control group. Pearson correlation and multiple regression method were used to investigate the relationship between urinary cadmium levels, gender, age, smoking, passive smoking, and minerals. Results The urinary cadmium level P50 (P25-P75) in exposed group was 5.45 (2.62-10.68)μg/g·cr, which was higher than that of the control group, which was 1.69 (1.22-2.36)μg/g · cr (Z=-10.49, P<0.001). The abnormal rate of urinary cadmium was 51.6%(80/155), which was higher than that of the control group (2.8%(4/143)) (χ2=87.56,P<0.001). The urinary Ca, Cu, Zn, and I level P50 (P25-P75) of exposed group were 173.80 (114.40-251.70), 20.55 (14.95-28.44), 520.23 (390.25-647.15), and 246.94 (203.65-342.97)μg/g · cr, which were higher than those in control group (142.42 (96.87-179.11), 15.44 (12.26-20.98), 430.09 (309.85-568.78) and 213.85 (156.70-281.63) μg/g · cr, respectively) (Z values were-4.33,-5.04,-3.47 and-4.24, all P values<0.001). The urinary P, K level P50 (P25-P75) of exposed group were 582.50 (463.20-742.8), 890.10 (666.00-1 305.40) μg/g · cr, which were lower than control group (694.50 (546.20-851.17), 1 098.58 (904.53-1 479.18) μg/g · cr) (Z values were-3.36,-4.02, all P values <0.001). on Based the results of Pearson correlation analysis, urinary cadmium was positively correlated with urinary Ca, Cu, Zn, and I, and the correlation coefficients were 0.31, 0.61, 0.38, and 0.25, respectively(all P values<0.05). Based on the results of multiple regression analysis, urinary cadmium levels contributed most to the metabolic balance of urinary Ca, Cu, Zn and I. The standardized regression coefficients were 0.31, 0.59, 0.39, and 0.24, respectively (all P values<0.001). Conclusion Long?term environmental exposure to cadmium affected the metabolic balance of Ca, Cu, Zn and I in human body.

Objective To investigate dynamic change of cadmium body burden and renal dysfunction among residents living in cadmium?polluted areas. Methods From April to July of 2011, the cadmium?polluted areas of northern Guangdong province in China was chosen as the study site. Based on the levels of cadmium pollution in soil and rice, the survey areas were divided into low exposed group (average concentration of cadmium was 0.15-0.40 mg/kg, 0.5-1.0 mg/kg in rice and soil, respectively) and high exposed group (average concentration of cadmium was >0.40 mg/kg, >1.0 mg/kg in rice and soil, respectively). Stratified random sampling and cluster sampling method of epidemiological investigations were carried out among 414 local residents who lived in cadmium exposure areas for more than 15 years, aged above 40, and without occupational cadmium exposure, including 168 and 246 residents in low and high exposed group, respectively. From March to June of 2014, 305 respondents of those who participated in 2011 were successfully traced, including 116 and 189 respondents in low and high exposed group, respectively. We used health questionnaires to acquire their health status. Home?harvested rice and vegetable samples were collected using quartering method for detection of cadmium level, including 190 rice samples, 161 vegetable samples in 2011 and 190 rice samples, 153 vegetable samples in 2014. Urine specimens of residents were collected for the detection of urinary cadmium and creatinine as well as renal dysfunction biomarkers, namely, N?acetyl?beta?D?glucosamidase (NAG) andβ2?microglobulin (β2?MG), respectively. In 2011 and 2014, Chi?square test was used to investigate the differences of abnormality of cadmium concentration in rice, vegetables and urinary cadmium,β2?MG,and NAG that were expressed as odds ratio (OR) and 95%confidence intervals (95%CI). Results In 2011 and 2014, cadmium concentration P50 (P25-P75) in rice was 0.43 (0.17-1.10) mg/kg,and 0.42 (0.20-1.14) mg/kg, respectively (Z=-0.77, P=0.440). In 2011 and 2014, cadmium concentrations P50 (P25-P75) in vegetables were 0.13 (0.07-0.34) mg/kg,and 0.25 (0.12-0.59) mg/kg, respectively, with abnormal rates of 38.5%(62/161) and 60.8%(93/153), respectively. In 2014, both average concentration and abnormal rate of cadmium in vegetables were higher than those in 2011 (Z=-4.69,P<0.001 andχ2=15.58, P<0.001). Concentrations of urinary cadmium P50 (P25-P75) in high exposed group were 7.90 (3.96-14.91)μg/g creatinine, 8.64 (4.56-17.60)μg/g creatinine in 2011 and 2014, respectively. Contrary to that in 2011, urinary cadmium of high exposed group was significantly increased in 2014 (Z=-2.80 ,P=0.005). In 2011 and 2014, concentrations of β2?MG, NAG P50 (P25-P75) were 0.15 (0.07-0.29)μg/g creatinine, 0.15 (0.07-0.45)μg/g creatinine,and 7.12 (5.05-10.65) U/g creatinine, 13.55 (9.1-19.84) U/g creatinine, respectively, with abnormal rates of 7.5% (23/305), 15.1% (46/305) ,8.2%(25/305) , and 33.8% (103/305), respectively. Compared with baseline in 2011, average concentrations ofβ2?MG, NAG significantly increased in 2014 (Z=-2.263,P=0.024 and Z=-12.52,P<0.001), and abnormal rates ofβ2?MG, NAG were also higher in 2014 (χ2=15.61,P<0.001 andχ2=64.72,P<0.001), with odds ratio (OR) of 2.00 (95%CI:1.23-3.24) and 4.12 (95%CI:2.87-5.92). Conclusion Environmental cadmium pollution of crops such as rice and vegetables in survey areas continued to remain high. Body burden of cadmium might kept at sustainably high levels and renal dysfunction was worsened after continuous, long?term cadmium exposure. Our results suggested that NAG might be more sensitive than β2?MG to serve as an indicator for an individual's future tubular function.

Evaluate the effect of the fresh air purification system on the improvement of indoor PM 2.5 levels in a primary school classroom in Jinan City, Shandong Province. Our purpose is to explore the optimal operating time of the fresh air system and the main factors that affect the fresh air purification system to improve indoor air quality. From December 9, 2019 to December 10, 2019, two classrooms of the same area on the third floor of a primary school building in Jinan City, Shandong Province were selected as monitoring points. During the operation of the fresh air purification system, the PM 2.5 concentration in the classroom is reduced by an average of 48.1%-61.5% compared to the outdoor PM 2.5 concentration. After running for about 2 hours, the indoor PM 2.5 concentration decreased to a relatively stable concentration level. The operating time of the fresh air purification system, student activities between classes, indoor temperature, indoor relative humidity, and outdoor PM 2.5 concentration are important factors that affect the indoor particulate removal rate. In the case of a certain amount of fresh air and indoor area, closing doors and windows and appropriately extending the operation time of the fresh air purification system can improve the air quality in the classroom to a certain extent and protect the health of students.