视觉能触发沟渠豹蛛雄蛛对雌蛛的求偶行为

以沟渠豹蛛Pardosa laura成熟雄蛛的求偶延迟时间和触肢伸展次数作为参数,观察研究了雄蛛通过视觉与处女雌蛛拖丝单独和共同诱导情况下的求偶反应,发现视觉是触发雄蛛求偶行为的主要信号,而雌蛛的拖丝则不能单独激发雄蛛的求偶行为,表明雄蛛能够通过视觉接受雌蛛的信号。在此基础上,又测定了雄蛛通过视觉接受亚成体雌蛛、处女雌蛛和交配未产卵雌蛛信号时的求偶反应,发现雄蛛对处女雌蛛和交配未产卵雌蛛的求偶动作次数显著多于亚成体雌蛛,表明雄蛛能够通过视觉区分雌蛛是否成熟,但是仅依靠视觉无法判断雌蛛是否已经交配。本实验表明视觉在沟渠豹蛛雄蛛对雌蛛识别过程中起着非常重要的作用,再次证实狼蛛的视觉比较发达。     

蜘蛛抗逆能力的研究

本文对隐蛛科的白斑隐蛛;狼蛛科的拟环纹豹蛛、星豹蛛、真水狼蛛、细毛水狼蛛;卷叶蛛科的猫卷叶蛛;栅蛛科的栓栅蛛;球蛛科的温室希蛛;皿蛛科的草间钻头蛛、难波小黑蛛、隆背微蛛、花腹盖蛛;园蛛科的黄斑园蛛;管巢蛛科的棕管巢蛛;蟹蛛科的三突花蛛;跳蛛科的吉蚁蛛等10科共16种蜘蛛做了在30 ℃恒温条件下的抗逆能力测定.结果表明,蜘蛛是一类抗逆能力较强的动物,只要供给水分,其雌蛛的平均寿命在25 d以上;水在蜘蛛生命活动中具有非常重要的作用,在相同的条件下,如果断食断水,蜘蛛的平均寿命显著缩短,只有6 d左右;由于蜘蛛种类和生活环境的不同,其耐饥饿的能力也表现出很大的差异,一般地面活动的蜘蛛或靠水边活动的蜘蛛耐饥、耐水能力较差,而游猎性蜘蛛,尤其是结网的蜘蛛抗逆能力较强;雌蛛的抗逆能力大于雄蛛;三突花蛛的耐饥能力随着龄期的增加而加强.     

中国狼蛛科的系统发育

运用分支分析法,采用支序分析软件Phylip程序,以盗蛛科和褛网蛛科为外群,从形态、生态等方面选取了18个特征对中国狼蛛11个属(脉狼蛛属未在其列)进行支序分析。分析结果表明,马蛛亚科(包括马蛛属和水狼蛛属)最为原始,潮浪蛛亚科次之;熊蛛属和獾蛛属构成的分支更次,狼蛛亚科和豹蛛亚科构成姊妹群最为进化。所以潮浪蛛属、熊蛛属和獾蛛属应分别从狼蛛亚科中独立出来,皆自成亚科,分别名潮浪蛛亚科和獾蛛亚科。     

温度对蜘蛛抗饥能力的影响

本文对隐蛛科的白斑隐蛛、狼蛛科的星豹蛛,栅蛛科的栓栅蛛,球蛛科的八斑鞘蛛,皿蛛科的花腹盖蛛,园蛛科的角类肥蛛,肖蛸科的鳞纹肖蛸,蟹蛛科的三突花蛛,管巢蛛科的粽管巢蛛,猫蛛科的斜纹猫蛛,跳蛛科的纵条蝇狮等11科11种蜘蛛的385头成蛛,296头2龄幼蛛和126头亚成蛛共计807头蜘蛛分别在20 ℃、25 ℃、30 ℃和35 ℃ 4种恒温条件下作了的抗饥能力研究.结果显示:(1)实验蜘蛛的2龄幼蛛、亚成蛛和成蛛抗饥能力的大小与温度的高低呈负相关,即随着温度的升高,抗饥能力减小.(2)由于蜘蛛种类不同,其抗饥能力的大小也表现出很大的差异.无论是2龄幼蛛还是成蛛,均以花腹盖蛛和鳞纹肖蛸抗饥能力最差;2龄幼蛛抗饥能力最强的是角类肥蛛;成蛛抗饥能力最强的是栓栅蛛、白斑隐蛛和角类肥蛛.(3)同一种蜘蛛,由于发育阶段不同其抗饥能力也表现出很大差异,随着蜘蛛发育阶段增长,其抗饥能力加强.在本实验条件下所有蜘蛛都是以2龄幼蛛抗饥能力较差,亚成蛛次之,成蛛的抗饥能力最强.     

中国微蛛亚科3新纪录属5新纪录种（蜘蛛目：皿蛛科）

记述了采自我国吉林省、新疆维吾尔自治区和湖北省皿蛛科微蛛亚科蜘蛛3新纪录属5新纪录种:双头蛛属,奇异双头蛛,盾大蛛属,尖盾大蛛;微玛蛛属,小突微玛蛛,双舟蛛属,叉胫双舟蛛,胫毛双舟蛛。     

花和田蜘蛛群落的研究

在花生田共采集到蜘蛛４１种,隶属于１２科、２７属。游猎型蜘蛛主要是狼蛛科、跳蛛科、猫蛛科和管巢蛛科的种类,所占比例较高,在春花生田为６０．９１～８６．２１％,秋药生田为５０．４０～９０．３６％。结网蜘蛛主要是皿蛛、珠蛛、肖蛸和小型园蛛。在花生的不同生长季节有不同的优势科和优势种。春花生男的优势科是狼蛛科、皿蛛科和猫蛛科,优势种是类水狼蛛、拟环纹豹蛛、脉蜗蛛、食虫沟瘤蛛和斜纹猫蛛;狼蛛科、猫蛛科和球     

花生田蜘蛛群落的研究

在花生田共采集到蜘蛛41种,隶属于12科、27属。游猎型蜘蛛主要是狼蛛科、跳蛛科、猫蛛科和管巢蛛科的种类,所占比例较高,在春花生田为60.91％～86.21％,秋花生田为50.40％～90.36％。结网蜘蛛主要是皿蛛、球蛛、肖蛸和小型园蛛。在花生的不同生长季节有不同的优势科和优势种。春花生田的优势科是狼蛛科、皿蛛科和猫蛛科,优势种是类水狼蛛、拟环纹豹蛛、脉娲蛛、食虫沟瘤蛛和斜纹猫蛛;狼蛛科、猫蛛科和球蛛科是秋花生田的优势科、脉娲蛛、斜纹猫蛛和八斑鞘蛛为优势种。     

贵州省茶园蜘蛛区系分布特征

经10多年考查和鉴定,记述了贵州省茶区蜘蛛26科204种,其中优势类群园蛛科50种、跳蛛科25种、肖蛸科20种、蟹蛛科14种、平腹蛛科13种,占总种数60%.全省性种类角类肥蛛、黄褐新园蛛、草间小黑蛛、食虫瘤胸蛛、三突花蛛、鞍形花蟹蛛、机敏蝇豹、纵条蝇狮、悦目金蛛、棒络新妇蛛、八斑鞘腹蛛、星豹蛛、棕管巢蛛、斜纹猫蛛、机敏漏斗蛛、浙江豹蛛、兰翠蛛、黑色蝇虎、茶色新园蛛和锥腹肖蛸等64种,占总种数31%.在我国动物区划中,贵州大部属于华中区的西部山地高原亚区,西部少数地区属于西南区的西南山地亚区.结合茶树适生格局,把茶园蜘蛛区系划分为:黔中山地丘陵区(Ⅰ)、黔东低山丘陵盆地区(Ⅱ)、黔南低山河谷区(Ⅲ)、黔北中山峡谷区(Ⅳ)、黔西高原中山区(Ⅴ).Ⅰ区发现蜘蛛21科137种,占全省总种数67%;常见的优势种有角类肥蛛、黄褐新园蛛、灌木新园蛛、青新园蛛和悦目金蛛等37种,占该区蜘蛛总种数27%;特有种为山地艾蛛、畸形艾蛛、对称曲腹蛛、西山新园蛛、小青新园蛛、四点亮腹蛛、桐庐指蛛、锯胸微蛛、黑底狼蛛、中华刺足蛛、裂额银斑蛛、贵州花蟹蛛和三斑花蟹蛛等13种.Ⅱ区发现蜘蛛26科185种,占全省总种数91%;优势种有角类肥蛛、棕管巢蛛、毁坏管巢蛛、斜纹猫蛛和三突花蛛等31种,占该区蜘蛛总种数17%;特有种有中华蟱蛛、棒络新妇蛛、四斑粗螯蛛、风雅丽蛛和江安七纺蛛等58种.Ⅲ区发现蜘蛛15科92种,占总种数45%;优势种为角类肥蛛、草间小黑蛛、食虫瘤胸蛛、驼背额角蛛和八斑鞘腹蛛等18种,占该区蜘蛛总种数20%.特有种为圆腹艾蛛、椭圆新园蛛、横带隆背蛛和凤振粗螯蛛等4种.Ⅳ区发现蜘蛛15科76种,占全省总种数37%;优势种为角类肥蛛、机敏漏斗蛛、机敏蝇豹、纵条蝇狮和黑色蝇虎等18种,占该区蜘蛛总种数24%.Ⅴ区发现蜘蛛14科64种,占总种数31%;优势种为角类肥蛛、黄褐新园蛛、机敏漏斗蛛、机敏蝇豹、黄斑菲蛛等15种,占该区蜘蛛总种数23%;Ⅳ和Ⅴ区无特有种类.Ⅲ区雨、热和光照条件较优越,但其为新辟茶区,蜘蛛种数少于Ⅰ和Ⅱ区.从西北部高寒山区向东部低丘,海拔明显降低,气候从北亚热带过渡到中亚热带,雨量、光照和积温加大,茶树等农林作物增多,茶园蜘蛛种类增多.     

青新园蛛的生物生态学研究

为调查青新园蛛的生物生态学特征,分别在田间和实验室条件下对其进行观察.如预期所示,幼蛛、亚成熟蛛和成蛛一起群居越冬.在湖南,青新园蛛每年可以繁殖3-4代,其中第4代寿命最长,第2-3代寿命最短.青新园蛛有织网的习性,雌蛛和雄蛛多次交配,一只雌蛛最多可产12个卵袋,每个卵袋平均含82.2颗卵粒.在群居模式中,刚孵化的蛛幼会安全的生活在雌蛛的背部.青新园蛛幼蛛的生长历期为40-120天,成蛛为33-176天.除第二代外,青新园蛛雌雄蛛的性别比率均小于1.该文详细描述了青新园蛛幼龄期和亚成熟期的生物学特征.在实验室条件下,青新园蛛的饥饿耐受力要强于抗旱力.     

中国数种熊蛛研究(蜘蛛目:狼蛛科)

记述我国狼蛛科熊蛛属５种,其中２新种为：沟谷熊蛛,三齿熊蛛,１种雄性新发现：湄潭熊蛛１９９３,中国２新纪录种;掠熊蛛富士熊蛛。     

Central nervous system effects of peptides, 1980-1985: a cross-listing of peptides and their central actions from the first six years of the journal Peptides

A tabular synopsis is presented for articles concerned with the effects of peptides on the central nervous system that appeared in the journal Peptides from 1980-1985. A table arranged alphabetically by peptide and one arranged by effects, both listing routes of injection, species, direction of change, and qualifying notes, provides easy cross-referencing of peptides and their effects. Over 80 peptides and over 135 effects are listed. The list of peptides includes, but is not limited to: ACTH, angiotensin, bombesin, bradykinin, calcitonin, casomorphin, CCK, ceruletide, CGRP, CRF, dermorphin, DSIP, dynorphin, endorphins, enkephalins, GRF, gastrin, LHRH, litorin, metkephamid, MIF-l, motilin, MSH, NPY, NT, oxytocin, ranatensin, sauvagine, substances P and K, somatostatin, TRH, VIP, vasopressin, and vasotocin. The list of effects includes, but is not limited to: aggression, alcohol, analgesia, attention, avoidance, behavior, cardiovascular regulation, catalepsy, conditioned behavior, convulsions, dopamine binding and metabolism, discrimination, drinking, EEG, exploration, feeding, fever, gastric secretion, GI motility, grooming, learning, locomotor behavior, mating, memory, neuronal activity, open field, operant behavior, rearing, respiration, satiety, scratching, seizure, sleep, stereotypy, temperature, thermoregulation and tolerance.     

蜜源油菜花粉有效成份的研究

油菜(Brassica campestrisLinn.var.oleifera DC.)花粉含有七种可溶性糖和一个中性多糖;十七种游离氨基酸和十八种水解氨基酸;十一种维生素;四种黄酮类化合物;九种脂肪酸;五种有机酸和廿二种矿质元素。因此,油菜花粉是一种营养与有效成份极其丰富的营养品。     

Chromosome numbers of Costa Rican grasses

Chromosome counts are presented for 217 species of 103 genera of grasses from Costa Rica. Four of the genera and 90 of the species are reported for the first time. In addition, 26 counts differ from previous records for the same taxon. The generaGynerium, Lithachne, Luziola, andThrasya were heretofore unknown cytologically. First counts are also given for the following species:Agrostis bacillata, A. pittieri, A. sub patens, Andropogon angustatus, A. bicornis, A. virgatus, Aristida capillacea, A. jorullensis, Arundinella berteroniana, A. deppeana, Axonopus aureus, A. capillaris, A. chrysoblepharis, Bouteloua americana, B. disticha, Bromus exaltatus, Calamagrostis intermedia, C. nuda, C. pittieri, Chusquea lehmannii, C. tonduzii, Cinna poaeformis, Deschampsia pringlei, Digitaria panicea, Echinochloa polystachya, Echinolaena gracilis, Eragrostis simplicijlora, Eriochloa distachya, E. polystachya, Eriochrysis cayennensis, Festuca dolichophylla, Gymnopogon fastigiatus, Gynerium sagittatum, Hymenachne amplexicaulis, Imperata contracta, Isachne polygonoides, Ischaemum latijolium, Lithachne pauciflora, Luziola fragilis, Manisuris aurita, Panicum aquaticum, P. arundinariae, P. boliviense, P. cordovense, P. grande, P. haenkeanum, P. milleflorum, P. parviglume, P. pilosum, P. polygonatum, P. rudgei, P. stenodes, P. trichanthum, P. trichoides, P. viscidellum, Paspalum candidum, P. centrale, P. decumbens, P. fasciculatum, P. jimenezii, P. microstachyum, P. multicaule, P. nutans, P. parviflorum, P. pilosum, P. prostratum, P. pumilum, P. reclinatum, P. saccharoides, P. scabrum, P. serratum, P. squamulatum, P. standleyi, Pennisetum bambusiforme, P. distachyum, Pereilema beyrichianum, Pharus parvifolius, Sacciolepis myuros, Schizachyrium condensatum, Sorghastrum incompletum, Sporobolus ciliatus, S. purpurascens, Streptochaeta sodiroana, Thrasya gracilis, T. petrosa, T. robusta, Trisetum pringlei, T. tonduzii, Uniola pittieri, and Zeugites pittieri. In addition, the following counts are different from previous records for the same taxon:Aegopogon cenchroides, Axonopus poiophyllus, Bouteloua media, Brachiaria plantaginea, Chusquea subtessellata, Digitaria adscendens, Homolepis aturensis, Hymenachne donacifolia, Ichnanthus axillaris, I. pallens, I. tenuis, Ischaemum ciliare, Ixophorus unisetus, Oplismenus burmannii, O. hirtellus, Panicum geminatum, P. glutinosum, P. mertensii, P. parvifolium, P. sellowii, Paspalum convexum, Pennisetum nervosum, P. setosum, Polypogon elongalus, Raddia costaricensis, Schizachyrium hirtijlorum.     

Intergeneric antigenic relation of Hafnia and Shigella (S. flexneri and S. boydii) bacteria

The O-antigenic relationships between Hafnia and Shigellae (S. flexneri and S. boydii) have been studied. For the first time the presence of antigenic relationship between Hafnia O19, O4, O9, O33, O5, O16, O12, O7, O29, O28, O10, O32, O24, O25, O18, O1, O13, O3, O22, O30, O37, O14, O11, O25, O23, O21, O28, O16, O24, O8, O26, O27 and S. flexneri la, lb, 2a, 2b, 4a, 4b, 6, 5a, 5b, as well as between Hafnia O10, O21, O35, O36, O9, O28, O8, O30 and S. boydii 1, 3, 6, 14, 2, 5, 2, 12 have been revealed. The character and degree of manifestation of antigenic relationships between the above-mentioned groups of bacteria have been established.     

东喜马拉雅地区多孔菌区系和生态习性

对东喜马拉雅地区多孔菌区系和生态习性进行了分析,发现该地区多孔菌极为丰富,共有10目19科101属372种,其中优势科为多孔菌科和锈革孔菌科,优势属为木层孔菌属和多孔菌属。种的区系地理成分可以分为8类,其中北温带类型种类最多,表明东喜马拉雅地区多孔菌具有明显的北温带区系特征。该地区的多孔菌有常见种、偶见种、稀有种和濒危种分别为156、141、54和21个;有腐生菌304种、寄生菌49种、菌根菌19种。在寄主方面,能够生长在被子植物上的有256种,裸子植物上的有137种,既能生长在被子植物,也能生长在裸子植物上的有40种,地上生长的有19种。东喜马拉雅地区的裸子植物,特别是云杉属、松属和冷杉属树木对于多孔菌的生长更重要,因为生长在这些属树木上的多孔菌分别有71、68和51种,高于该地区被子植物其他属树木上的多孔菌。     

Significance of Trace Element Profile of Blood of Persons with Multiple Caries versus Sound Teeth

In order to determine any possible relation between chemical composition of a person’s blood to formation of dental caries, whole blood was analyzed for 35 inorganic elements (Si, Al, Fe, Ca, Mg, K, Mn, Ti, P, Li, Be, B, V, Cr, Co, Ni, Cu, Zn, As, Sr, Y, Nb, Mo, Ag, Cd, Sn, Sb, Ba, La, Ce, W, Pb, Bi, Zr, and F) in the 15 people having sound teeth as well as an equal number of those having multiple caries. The results showed the absence of 13 elements (Si, Al, Mn, Ti, Be, Co, As, Y, Cd, Ba, La, Ce, and Zr) in the blood of both groups. Of the remaining 22 elements, the results of only seven elements (Fe, P, B, V, Sr, Sn, and F) were significantly different between the two groups. The most remarkable finding of this study was significantly decreased amount of phosphorus, strontium, and fluorine and perhaps increased boron in the blood of persons with caries.     

Erhardorina n. g., Ascogregarina polynesiensis n. sp., Eimeria golemanskii n. sp., Isospora tamariscini n. sp., Gregarina kazumii n. nom., new combinations and emendations in the names of apicomplexan protozoa

On the basis of a review of the approximately 4300 species of apicomplexan protozoa, the following new species, new names, new combinations, and emendations are given: NEW GENUS, Erhardovina; NEW SPECIES, Ascogregarina polynesiensis, Eimeria golemanskii, Isospora tamariscini; NEW NAME, Gregarina kazumii; NEW COMBINATIONS, Ascogregarina brachyceri (Purrini, 1980), Erhardovina euzeti (Lipa, 1981), E. scutovertexi (Erhardová, 1955), Haemorhormidium batrachi (Chaudhuri & Choudhury, 1983); EMENDATIONS, Selenidium francianum (Arvy, 1952) Tuzet & Ormières, 1965, Pyxinioides bolitoides D. P. Henry, 1938, P. japonicus H. Hoshide, 1951, P. kamenote H. Hoshide, 1951, P. kurofuji H. Hoshide, 1951, P. oshoroensis H. Hoshide, 1951, P. pugetensis D. P. Henry, 1938, Gregarina levinei Haldar & Sarkar, 1980, Retractocephalus halticae Haldar, Chakraborty & Kundu, 1982, Cnemidospora schizophylli Tuzet & Guerin, 1947, Grebneckiella indica (Merton, 1911) Watson, 1916, Quadruspinospora atractomorphae Haldar & Chakraborty, 1978, Haemogregarina acipenseri Nawrotzky, 1914, H. lobianci Yakimov & Kohl-Yakimov, 1912, H. yakimovikohlae Wladimiroff, 1910, Hepatozoon luehi (Sambon, 1909) Pessoa, Cavalheiro & de Souza, 1970, Eimeria beyerae Ovezmukhammedov, 1977, E. (?) gigantea (Labbé, 1896) Reichenow, 1921, E. (?) labbei Hardcastle, 1943, E. rufi Prasad, 1960, E. (?) scylii (Drago, 1902) Levine & Becker, 1933, Isospora corvi Ray, Shivnani, Oommen & Bhaskaran, 1952, I. melopsittaci Bhatia, Chauhan, Arora & Agrawal, 1973, I. seicerci Ray, Shivnani, Oommen & Bhaskaran, 1952, I. stomatici Chakravarty & Kar, 1944, I. triffitae Nukerbaeva & Svanbaev, 1973, Wenyonella mackinnonae Misra, 1947, Octosporella sanguinolentae Ovezmukhammedov, 1975, Lankesterella millani Alvarez Calvo, 1975, Sarcocystis woodhousei Dogel', 1916, Haemoproteus lari Yakunin, 1972, Babesia ninakohlyakimovae (Yakimoff & Shokhor, 1916), Theileria ninakohlyakimovae (Yakimov, 1916) Krylov, 1974, Haemohormidium batrachi (Chaudhuri & Choudhury, 1983).     

Are Metals Accumulated in Human Hair Affected by Naturally Occurring Asbestos Fiber Contamination? A Case Study from a Rural Area of China

Little is known about the link between metals accumulated in human and asbestos fiber contamination in the environment. Therefore, hair samples of 368 subjects (128 males and 240 females) from a rural area contaminated by crocidolite asbestos fibers were collected to investigate the distributions of 17 metals accumulated in human. The results showed that the mean concentrations of As, Al, Ba, Cd, Co, Cr, Cu, Fe, Hg, Mg, Mn, Mo, Na, Ni, Pb, Sr, and Zn in hair of the total subjects were 0.23, 23.36, 4.33, 0.11, 0.05, 0.70, 10.53, 29.74, 0.37, 241.57, 3.52, 0.08, 153.21, 0.72, 4.26, 10.96, and 113.35 mg/kg, respectively. Moreover, approximately 86.14, 52.17, 73.91, 85.05, 80.98, 74.46, and 53.80 % of the hair samples of the total subjects contained much higher concentrations of Al, Ba, Fe, Mg, Mn, Na, and Sr compared with the highest reference values, respectively. The mean concentrations of the determined metals (except for As, Co, Cr, Hg, and Mo) significantly varied among different age groups for both male and females. The results of correlation analysis and cluster analysis revealed that strong correlations were found between Al, Fe, Zn, Mg, and Na accumulated in human from the study area. These might suggest that Al, Ba, Fe, Mg, Mn, Na, and Sr were significantly derived from contamination of crocidolite asbestos fibers. Zn, Mg, and Na might also originate from diet. However, Cd, Mo, Co, As, Cr, Hg, Ni, Mn, Pb, and Ba accumulated in human seemed to be mainly derived from soil. It can be concluded that metals accumulated in human hair have a link with asbestos fiber contamination in the environment.     

Multitracer study on biosorption of trace elements in yeastSaccharomyces cerevisiae

To estimate the applicability of yeastSaccharomyces cerevisiae as a radioisotope accumulator, biosorption of 18 radionuclides (isotopes of Be, Na, Sc, V, Cr, Mn, Fe, Co, Zn, As, Se, Rb, Sr, Y, Zr, Tc, Ru, and Rh) by the cells was tested using a multitracer technique. This technique enables us to examine the uptake of various elements under an identical condition. We showed that the yeast has ability to take up radioactive tracers of Be, Sc, V, Cr, Mn, Fe, Co, Zn, As, Se, Sr, Y, Zr, Ru, and Rh from an aqueous environment. Tracers of Be, Sc, Mn, Co, Zn, Se, Sr, Y, and Zr were distributed in both cell walls and other cell parts. Moreover, tracers of Sc, Mn, Co, Zn, Se, Sr, and Y were present as soluble and insoluble forms, and most of the Be and Zr were present as an insoluble form in the cells.