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2011Estimation of 210Po and 210Pb and its dose to human

Estimation of 210Po and 210Pb and its dose to human beings due to consumption of marine species of Ennore Creek,South India

M.Saiyad Musthafa &R.Krishnamoorthy

Received:8May 2010/Accepted:14October 2011#Springer Science+Business Media B.V .2011

Abstract A systemic study on the natural radio-nuclides such as 210Po and 210Pb in the environmental matrices and biota of Ennore Creek has been undertaken to establish a baseline data on the radiation profile of Ennore Creek environment.The environmental samples such as water,sediment,and biota (seaweeds,molluscs,crustaceans,and fishes)have been subjected to analyses.It has been observed that the concentration of 210Po and 210Pb in the water samples of Ennore Creek as 2.7and 1.63m Bq L ?1,respectively.The activity concentration of 210Po and 210

Pb in the sediment sample was 17.9and 28.9Bq kg ?1,respectively.The bivalve mollusk Perna viridis have been identified to accumulate higher concentrations of 210Po and 210Pb suggesting that they could serve as bioindicator of radionuclides in the Ennore Creek environment.The committed

effective dose for human beings was found at 81.13–216.8and 2.1–297.2μSv year ?1for 210Po and 210Pb,respectively.

Keywords Ennore Creek .Natural radionuclides .Committed effective dose .Biota

Introduction

210

Po,a high-energy α-particle emitter in the 238U decay chain,is accumulated in very high levels in marine organisms and in fact is responsible for the majority of the internal radiation dose (Cherry and Heyraud 1981;Carvalho 1988).Furthermore,because of these high accumulations of 210Po,which occur in the edible portions of marine organisms,210Po is considered to be the most important contributor of radiation dose received by humans via fish and shellfish consumption (Aarkrog et al.1997).

The consumption of marine foodstuffs contain-ing radioactivity,including fish,seaweeds,and manufactured products,is ordinarily the exposure pathway of greatest importance.The levels of radionuclides in the edible portions of marine plants and animals may be many times higher than that in the seawater because of biological

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DOI

10.1007/s10661-011-2417-8

M.S.Musthafa (*)

Post Graduate and Research Department of Zoology,The New College,

Chennai 600014,Tamilnadu,India

e-mail:saiyad_musthafa@https://www.doczj.com/doc/f74276341.html,

R.Krishnamoorthy

Department of Biotechnology,Bharathidasan University,Tiruchirappalli 620024,Tamilnadu,India

reconcentration processes.Among the natural radionuclides occurring in the oceans,alpha emit-ters are considered the most important with respect to potential internal radiation exposure of living tissues.A large contribution to the radiation dose received by marine fauna comes from members of the naturally occurring uranium series accumulated in the body,especially polonium as210Po(Cherry et al.1994).210Po is found to be the major contributor (90%)to the natural radiation dose coming from alpha-emitting radionuclides received by most marine organisms(McDonald et al.1993).

The accumulation of210Po in marine organisms is generally derived from the food chain(Carvalho and Fowler1993),and significant differences in the amount of210Po have been noted in various marine species.For example,2.4Bq kg?1wet weight in fish, 15Bq/kg wet weight in molluscs,and6Bq kg?1wet weight in crustaceans have been computed as“glob-al”average concentrations of210Po in the edible fraction of these types of organisms(Aarkrog et al. 1997).Especially high levels of210Po have been observed in the individual tissues and organs of these species such as the digestive track of fish,the digestive gland of molluscs,and the hepatopancreas of crustaceans;these levels of210Po are generally one to two orders of magnitude higher than in the muscle of these species(Cherry et al.1983;Skwarzec and Falkowski1988;Stepnowski and Skwarzec2000). The concentration and distribution of210Pb,210Po, and226Ra have been studied extensively in the biosphere and more particularly in the human envi-ronment(Osborne1963;Beasely and Palmer1966; Schell et al.1973).Studies on210Pb is particularly important because the amount of the daughter210Bi and210Po in the human and animal(Holtzman1996). The occurrences of210Pb in the environment have been recognized for more than50years.Since it is an ubiquitous component of the natural radiation envi-ronment and hence it is present almost in all abiotic and biotic component leading to direct and indirect human radiation exposure(Holtzman1996),the210Pb is strongly accumulated by organisms and transferred via food along a trophic chain(Cherry and Shannon 1974;Skwarzec and Falkowski1988).The internal dose delivered by210Pb to the general population is important relative to other hazardous radionuclides in environment.There is no systemic data for natural radionuclides in the biota of Ennore Creek.This present baseline study determines the concentrations in biota and committed effective dose due to210Po and210Pb.

Materials and methods

Study area

Physiographic setting

Ennore Creek(latitude13°15′N and longitude80°19′E)is a fresh/brackish water system,which is nearly 800m wide and elongated in a NE–SW direction (Fig.1).Ennore Creek is complex,the average depth rarely exceeding5m in the non-monsoon period, being fed by Koratalaiyar River and the Buckingham Canal;it is also connected to the Pulicat brackish water lake on the northern side,which once nurtured rich fauna and flora,including mangroves.The Ennore Creek flows from the west to east and open into the Bay of Bengal.It is located in the northeastern part of Chennai,Tamil Nadu,India and is spread over an area of4km2along the coast of Bay of Bengal.

The Ennore Creek is the estuary of the river Kortaliar,which is an outlet for the excess water from the Poondi reservoir.The Ennore Creek flows from the west to east and open into the Bay of Bengal,at Ennore.

Sample collection and process

Samples of water,sediment,seaweeds(Gracilaria edulis,Ulva reticulata,and Sargasum wightii),crus-taceans(Penaeus indicus and Penaeus monodon), bivalves(Perna viridis,Mytilus edulis,and Mytilius gravincia provincialis),and fish(Sacinella fimbriata and Tilapia mossambica)were collected(each sample taken seven times)from the Ennore Creek.The biological samples were washed thoroughly with distilled water to free them from attached sand/silt owing to high radionuclide association with silt/ detritus materials.The soft tissue and muscle from shell and bone were separated in molluscan,crusta-cean,and fish.The wet weights of the samples were recorded and then dried in an oven at110°C overnight to obtain the dry weights.

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Fig.1Map showing the study area

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210Po analysis

Water

Approximately50L of water was filtered through pre-weighted Whatman?cellulose filter paper(pore size0.45μm)and acidified with concentrated HCl to pH1.Fe3+carrier(500mg)was added to the filtered and acidified sample and the210Po in the filtered water was collected on Fe(OH)3by slow addition of concentrated ammonium hydroxide with rapid stirring until pH reached9.Two repeat precipitations were carried out to completely carry210Po activity by Fe (OH)3.The precipitate was dissolved in0.5N HCl and210Po deposited on both sides of a polished silver planchette by electrochemical deposition technique. Alpha counting was carried out following the procedure of Flynn(1968)and Iyengar et al.(1980).

Analysis of210Po in biota

The biota samples were dried,homogenized,and transferred to a400-ml beaker and repeatedly digested with a concentrated HNO3:H2O2(1:1) oxidizing mixture until a white ash was obtained. The residue was evaporated with concentrated HCl repeatedly to convert to chloride medium,then taken up in0.5N HCl and210Po was plated on a silver planchette by electrochemical deposition method and the activity was alpha counted following the method given below.

Electrochemical deposition of210Po

The sample solution in0.5N HCl was placed on a magnetic stirrer with thermostat control at a temper-ature of90°C.Ascorbic acid(100mg)was added to reduce ferric ions to ferrous,thus eliminating its interference in electrochemical deposition of poloni-um.A silver planchette(0.8-mm thickness and2.5-cm diameter)of predetermined background and whose both sides were brightly polished with emery paper was suspended in the sample solution by means of a nylon thread at the end of a glass rod,connected to a stirrer.The silver planchette was kept spinning for a period of5–6h with the aid of the stirrer.Spontane-ous deposition of210Po on both sides of the silver planchette took place under these conditions.At the end of the plating period,the planchette was taken out,rinsed with alcohol,dried under infrared lamp for few minutes,and counted for activity on both sides in an alpha counter.Deposition efficiency of210Po on biological samples spiked with uranium ore solution containing equilibrium activity of210Po using the above method yielded a recovery range varying from 95%to100%with an average efficiency of98±2%. The counting instrument used was a Radiation Counting System(ECIL-RCS4027-A)with an alpha counter of ZnS(Ag)detector(ECIL-SP647-A) having a background of0.1–0.2cpm and a counting efficiency of25–28%for239Pu(244.4dpm)standard source.

210Pb analysis

Water

Water(~100L)was filtered through pre-weighted Whatman?cellulose filter paper(pore size0.45μm) and passed through ferric hydroxide-impregnated acrylic fiber(25g)packed in a glass column at a flow rate of50–60ml/min(Krishnaswamy et al. 1972).After complete passage of the river water,the column was washed with distilled water,and the fiber was transferred to a500-ml beaker containing hot8N HCl.The fiber was kept immersed for some time to leach out the ferric hydroxide matrix containing210Pb and other radioelements that have strong affinities for adsorption.Treatment of the ferric hydroxide-coated fiber with hot8N HCl was continued until the fiber was bleached white.The leachate was evaporated to dryness on a hot plate,followed by dissolution of the residue in2M HNO3and made up to50ml.This solution was then used for the determination of210Pb via its beta-emitting daughter(Iyengar et al.1980; Kamath et al.1964).

Analysis of210Pb in biota

The biota samples were dried,homogenized,and repeatedly digested with a concentrated HNO3+ H2O2(1:1)mixture to achieve complete decomposi-tion until a white ash was obtained.The residue was leached with2N HNO3,filtered,and made up to 50ml.This solution was then used for210Pb determination.

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Determination of210Pb

To the above-mentioned solution(50ml),Pb carrier (100mg),and Ba carrier(10mg)were added and boiled.Sulfates were then precipitated with9N H2SO4.The210Pb carried on the Ba(Pb)SO4 precipitate was dissolved in ammoniacal EDTA. Barium sulfate was then precipitated with acetic acid leaving the carrier Pb and210Pb in solution.The solution was stored for50days to allow for the growth of210Bi.Bismuth carrier(10mg)and Ca carrier(200mg)were then added and Bi(OH)3was precipitated with ammonia.Then,Bi(OH)3was dissolved in0.5N HNO3.The210Bi was then precipitated with H3PO4as BiPO4,which was then washed,dried,and counted for beta activity in a special type of low background beta-counting system. The counting system consisted of a gas flow type GM counter with argon as the counting gas and isopropyl alcohol vapor as the quenching agent.Coincidence and anticoincidence technique was used to reduce the background.A15-cm thick lead shield surrounding the detector also reduced the background consider-ably.The background of the counting system was 1.5–2.0cpm,with a counting efficiency of40%for 40K beta energy.The sample purity was checked by following up the210Bi decay over a120-h period,and the final activity was calculated by applying the necessary corrections for decay,chemical recovery (80±4%),date of sampling,etc.Spiked experimental recoveries on water and biological samples using the above method yielded an overall efficiency of90%.

Committed effective dose calculations

Committed effective doses(CEDs)were calculated using conversion factors(in sieverts per becquerel) for adults adopted in the coordinated project MAR-DOS(IAEA1995),namely,4.3×10?8for210Po and 6.9×10?7for210Pb.Therefore,the dose calculations proceeded using the following formulas:

D Poà120?4:3?10à7?C Poà210?Ire1T

D Pbà210?6:9?10à7?C Pbà210?Ire2Twhere D Po?210and D Pb?210are the CED values for 210Po and210Pb,respectively(in sievert per year),C Pb?210and C Po?210are the radionuclide concen-trations in the edible part of fish(in becquerels per kilogram wet weight),and Ir is the ingestion rate(in kilograms per year).The ingestion rate used for biota is the international mean(FAO1999)equal to 4.45kg year?1.

Results and discussion

The activity concentration of210Po and210Pb mea-sured in the water,sediment,and biota(seaweeds, molluscs,crustaceans,and fishes)was collected from Ennore Creek,South India is given in Table1.All the results are discussed on the basis of dry weight.

The210Po and210Pb concentration in the water sample of Ennore Creek was found to be2.7and1.63m Bq L?1,respectively.Bukhari et al.(2003)reported that the210Po and210Pb activity in coastal water of Palk Strait mean valve was1.54and3.15mBq L?1. These values are lesser than the Gulf of Mannar coastal water(34.18mBq L?1)(Somasundaram 1998).The activity concentration of210Po and 210Pb in the sediment sample was17.9and 28.9Bq kg?1,respectively.The reported210Pb value is higher than the value recorded in Kalpakkam beach (3.2Bq kg?1)which is less when compared to the Gulf of Mannar sediment(35.3Bq kg?1)and Kalpakkam beach sediment(385Bq kg?1;Iyengar et al.1980).

Three species of seaweeds(https://www.doczj.com/doc/f74276341.html,lis,U.reticulata, and S.wightii)were analyzed for210Po and210Pb the concentration which ranged from19.6to 32.1Bq kg?1and from2.0to4.7Bq kg?1,respec-tively.The concentrations of210Po and210Pb in the seaweed were found to be in the range of 5.90–20.0Bq kg?1and1.35–1.98Bq kg?1,respectively (Bukhari et al.2003).Among the seaweeds,S.wightii displayed high activity of210Po level(20.00Bq kg?1) than the others.The recorded values are lower with the values reported by Masilamani(2001).The accumulation of210Pb was,however,significantly lower than that of210Po in all the species of seaweeds examined.It was observed that Hypena sp.was found to have Pb-210in higher concentration(1.98Bq kg?1) than the others.

In the present study,the bivalves(P.viridis,M. edulis,and M.gravincia provincialis)accumulated the highest concentration(96.12–113.32Bq kg?1and

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25.42–96.80Bq kg?1)of210Po and210Pb respectively in the Ennore Creek environment.The maximum concentrations of these radionuclides were observed in P.viridis species.Bukhari et al.(2003)observed that the soft tissue recorded a high level of210Po (33.70–345.20Bq kg?1)and shell recorded a high level of210Pb210(6.30–12.10Bq kg?1).The bivalves are used as indicator of pollutants such as heavy metals,pesticides,and radionuclides in the environment for the reason that suspension feeding bivalve mollusks are capable of accumulating con-taminants in biological system(Forester1980).

The concentration of210Po and210Pb in the crustaceans(P.indicus and P.monodon)was ranged between42.4and61.3Bq kg?1and0.7and 1.4Bq kg?1,respectively.Hameed(2001)reported that the Crustacean muscle recorded a high level of 210Po(41.3–89.4Bq kg?1)and exoskeleton recorded a high level of210Pb(40.2–51.6Bq kg?1).It is suggested that the presence of organic moiety such as chitin is responsible for the higher level of210Po in crustaceans.Cherry and Heyraud(1981)states that 210Po has higher binding affinity for organic moiety and possibly accounting for the high activity of210Po in the exoskeleton of crustacean.

The concentration of210Po and210Pb in the fishes (S.fimbriata and T.mossambica)ranged from41.3to 81.6Bq kg?1and from0.72to2.0Bq kg?1.The concentration of210Po in fish muscle was in the range from20.8to181.3Bq kg?1and in bone from12.6to 102.2Bq kg?1(Krishnamoorthy et al.2006b).In this present study,the higher concentration of210Po and 210Pb observed in bivalves could possibly due to their benthic mode of life and detritivore feeding,which tend to accumulate enormously.Germain et al.(1995) reported that the210Po concentrations in the https://www.doczj.com/doc/f74276341.html,lis ranged from90to700Bq kg?1in the English Channel Coast environment of France.This concen-tration was very high when compared with the present study.The210Po and210Pb concentrations in the edible tissues of biota are higher in the present study than reported for biota in the Palk Strait Coastal environment,India(Suriyanarayanan et al.2008)and Marshall Island,USA(Noshkin et al.1994).The values of210Po and210Pb concentrations were higher in the present study than those reported for fishes in the marine environments of Japan and Syria(Yamamoto et al.1994;Al-Masri et al.2000).

The annual dose received by the general public via ingestion of210Po through dietary components is

Table1The concentration of210Po and210Pb and environmental matrices and biota of Ennore Creek,South India Species Activity concentration(Bq kg?1)Committed effective dose(μSv year?1)

210Po (mBq L?1)210Pb

(mBq L?1)

210Po210Pb

Water 2.70±1.24 1.63±0.62––

Sediment17.9±1.328.9±1.7––

Seaweeds

Gracilaria edulis13.6±1.7 2.5±0.21––

Ulva reticulata32.1±2.1 4.7±1.17––

Sargasum wightii19.6±2.2 2.0±0.43––

Bivalves

Perna viridis113.32±7.1096.80±5.25216.8297.2

Mytilus edulis96.12±5.2225.42±1.73183.9278.1

Mytilus gravincia provincialis101.90±5.9049.42±3.08195.7151.74

Prawn

Penaeus indicus61.3±4.3 1.4±0.26117.3 4.3

Penaeus monodoan42.4±2.10.7±0.2281.13 2.1

Fishes

Sarcinella fimbriata41.3±3.10.72±0.3679.03 2.2

Tilapia mossambica81.6±6.7 2.0±0.62156.1 6.1

±standard deviation(number of samples,7)

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important from the fact considerable variations in the intake levels of210Po(Holtzman1996).Radiation dose deposition in human body due to consumption of seafood can be estimated by two methods(IAEA 1995).The first is based on the210Po and210Pb concentrations in the marine water of the fishing areas.The second method is based on the210Po and 210Pb concentrations in the edible tissues of fish.The committed effective dose was found to be79.03–216.8μSv year?1and2.1–297.2μSv year?1for210Po and210Pb,respectively.Krishnamoorthy et al.(2006a) reported that the higher210Po dose is expected via the consumption of fish Sardinella longicepes (552.1μSv year?1)in Athangarai estuary and Thryssa malabarica(406.9μSv year?1)in Punnai-kayal estuary.The CED to the public from210Po due to consumption of seafood from Bombay Harbour bay(2.1–40.0μSv year?1)and Kalpakkam environ-ment(36.3μSv year?1)were lower than the present study reported by Bangera and Rudran(1995)and Rajan et al.(1980).The present study indicated that the dose transfer to the inhabitants of the Ennore Creek through210Po intake was higher when compared to those in Bombay coast and Kalpakkam coast.

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Environ Monit Assess

从实践的角度探讨在日语教学中多媒体课件的应用

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新视野大学英语全部课文原文

Unit1 Americans believe no one stands still. If you are not moving ahead, you are falling behind. This attitude results in a nation of people committed to researching, experimenting and exploring. Time is one of the two elements that Americans save carefully, the other being labor. "We are slaves to nothing but the clock,” it has been said. Time is treated as if it were something almost real. We budget it, save it, waste it, steal it, kill it, cut it, account for it; we also charge for it. It is a precious resource. Many people have a rather acute sense of the shortness of each lifetime. Once the sands have run out of a person’s hourglass, they cannot be replaced. We want every minute to count. A foreigner’s first impression of the U.S. is li kely to be that everyone is in a rush -- often under pressure. City people always appear to be hurrying to get where they are going, restlessly seeking attention in a store, or elbowing others as they try to complete their shopping. Racing through daytime meals is part of the pace

新视野大学英语第三版第二册课文语法讲解 Unit4

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新视野大学英语读写教程第一册课文翻译及课后答案

Unit 1 1学习外语是我一生中最艰苦也是最有意义的经历之一。虽然时常遭遇挫折,但却非常有价值。 2我学外语的经历始于初中的第一堂英语课。老师很慈祥耐心,时常表扬学生。由于这种积极的教学方法,我踊跃回答各种问题,从不怕答错。两年中,我的成绩一直名列前茅。 3到了高中后,我渴望继续学习英语。然而,高中时的经历与以前大不相同。以前,老师对所有的学生都很耐心,而新老师则总是惩罚答错的学生。每当有谁回答错了,她就会用长教鞭指着我们,上下挥舞大喊:“错!错!错!”没有多久,我便不再渴望回答问题了。我不仅失去了回答问题的乐趣,而且根本就不想再用英语说半个字。 4好在这种情况没持续多久。到了大学,我了解到所有学生必须上英语课。与高中老师不。大学英语老师非常耐心和蔼,而且从来不带教鞭!不过情况却远不尽如人意。由于班大,每堂课能轮到我回答的问题寥寥无几。上了几周课后,我还发现许多同学的英语说得比我要好得多。我开始产生一种畏惧感。虽然原因与高中时不同,但我却又一次不敢开口了。看来我的英语水平要永远停步不前了。 5直到几年后我有机会参加远程英语课程,情况才有所改善。这种课程的媒介是一台电脑、一条电话线和一个调制解调器。我很快配齐了必要的设备并跟一个朋友学会了电脑操作技术,于是我每周用5到7天在网上的虚拟课堂里学习英语。 6网上学习并不比普通的课堂学习容易。它需要花许多的时间,需要学习者专心自律,以跟上课程进度。我尽力达到课程的最低要求,并按时完成作业。 7我随时随地都在学习。不管去哪里,我都随身携带一本袖珍字典和笔记本,笔记本上记着我遇到的生词。我学习中出过许多错,有时是令人尴尬的错误。有时我会因挫折而哭泣,有时甚至想放弃。但我从未因别的同学英语说得比我快而感到畏惧,因为在电脑屏幕上作出回答之前,我可以根据自己的需要花时间去琢磨自己的想法。突然有一天我发现自己什么都懂了,更重要的是,我说起英语来灵活自如。尽管我还是常常出错,还有很多东西要学,但我已尝到了刻苦学习的甜头。 8学习外语对我来说是非常艰辛的经历,但它又无比珍贵。它不仅使我懂得了艰苦努力的意义,而且让我了解了不同的文化,让我以一种全新的思维去看待事物。学习一门外语最令人兴奋的收获是我能与更多的人交流。与人交谈是我最喜欢的一项活动,新的语言使我能与陌生人交往,参与他们的谈话,并建立新的难以忘怀的友谊。由于我已能说英语,别人讲英语时我不再茫然不解了。我能够参与其中,并结交朋友。我能与人交流,并能够弥合我所说的语言和所处的文化与他们的语言和文化之间的鸿沟。 III. 1. rewarding 2. communicate 3. access 4. embarrassing 5. positive 6. commitment 7. virtual 8. benefits 9. minimum 10. opportunities IV. 1. up 2. into 3. from 4. with 5. to 6. up 7. of 8. in 9. for 10.with V. 1.G 2.B 3.E 4.I 5.H 6.K 7.M 8.O 9.F 10.C Sentence Structure VI. 1. Universities in the east are better equipped, while those in the west are relatively poor. 2. Allan Clark kept talking the price up, while Wilkinson kept knocking it down. 3. The husband spent all his money drinking, while his wife saved all hers for the family. 4. Some guests spoke pleasantly and behaved politely, while others wee insulting and impolite. 5. Outwardly Sara was friendly towards all those concerned, while inwardly she was angry. VII. 1. Not only did Mr. Smith learn the Chinese language, but he also bridged the gap between his culture and ours. 2. Not only did we learn the technology through the online course, but we also learned to communicate with friends in English. 3. Not only did we lose all our money, but we also came close to losing our lives.

教案检查记录情况记录

教案检查记录情况记录 精品文档 教案检查记录情况记录 根据学校安排,由教导处组织,学校领导、各教研组长参加,对2013年春季 开学至3月22号期间的教师教案和学生作业情况进行了检查,检查情况汇总如下: 语文组: 本次教案编写课时量充足,设计合理,结构完整,详略得当,作业次数充足, 批注认真,有评语。特别是杨焕荣、尹秋菊等老师的教案内容充实,书写认真,反 思深刻。 数学组: 各教师教案编写认真,规范,内容充实,环节完整,有教学反思。且能从实际 出发,由感而发,作业批改及时,有详细的批注,评语。简亚丽、何修建、王新爱 等老师,教案编写、作业批改很认真 英语组: 通过检查英语组全体教师都能认真备课且设计合理,条理清楚,书写工整。写 有反思的有楚玉莉、董玉玲、余为勇、陈海云老师。作业形式多样,批改认真,董 玉玲、孙俊老师全批全改且有鼓励性语言的有余为勇,存在问题是个别教师备课量 虽足但过于简单,没写课后反思。 政史地组: 本次检查中,教案编写都较认真,及时,足额,且内容较为充实,完备,结构 完整,书写认真,反思深刻,设计 1 / 12 精品文档

操作性强,方法多样,体现了新课改理念,作业批改较及时认真,个别同志有 针对性评语,对学生进行详细评价,具有很大的促进作用。但也有个别同志教案过 于简单,不能完全体现新课改要求,设计不十分合理,需要大力改进。 理化生组: 大多数教师多为详案,书写认真,结构完整,节节有反思。作业有批有改,极 个别教师部分教案书写有点简单,内容空洞。 通过各组反馈情况,总结如下: 好的方面 1(总体检查情况良好,绝大多数老师能根据所任学科教材及班级实际备课、编 写教案,课时教案目标突出,渗透了新课程理念,以人为本,面向全体,积极倡导 自主、合作、探究的教学模式,有一定教学准备,过程清晰。 2(大部分老师的教案具有内容规范、项目填写齐全、突出重难点等优点,还体 现了学习方法、课后练习具有实效性,学习形式多样性的特点。 3(多数老师能根据教学对象和所教科目的不同、科学设计教案、能根据不同年龄、不同层次的学生,采取不同的内容和进度。 4(教学反思有一定的量,大部分老师课后发现有更好的上课思路、方法,能及 时写的备课本上,补上去或修改 2 / 12 精品文档 好,使下次备课更加完美,较有效地达到了反思的目的。 5多数教师能够认真对待作业的布置及批改这一环节;批改及时、认真,对于作业完成出色或有进步的学生能够给出激励性的评语,调动了学生的积极性;模块测试,单词测试,课文背诵检查到位及时. 存在的问题

新大学日语简明教程课文翻译

新大学日语简明教程课文翻译 第21课 一、我的留学生活 我从去年12月开始学习日语。已经3个月了。每天大约学30个新单词。每天学15个左右的新汉字,但总记不住。假名已经基本记住了。 简单的会话还可以,但较难的还说不了。还不能用日语发表自己的意见。既不能很好地回答老师的提问,也看不懂日语的文章。短小、简单的信写得了,但长的信写不了。 来日本不久就迎来了新年。新年时,日本的少女们穿着美丽的和服,看上去就像新娘。非常冷的时候,还是有女孩子穿着裙子和袜子走在大街上。 我在日本的第一个新年过得很愉快,因此很开心。 现在学习忙,没什么时间玩,但周末常常运动,或骑车去公园玩。有时也邀朋友一起去。虽然我有国际驾照,但没钱,买不起车。没办法,需要的时候就向朋友借车。有几个朋友愿意借车给我。 二、一个房间变成三个 从前一直认为睡在褥子上的是日本人,美国人都睡床铺,可是听说近来纽约等大都市的年轻人不睡床铺,而是睡在褥子上,是不是突然讨厌起床铺了? 日本人自古以来就睡在褥子上,那自有它的原因。人们都说日本人的房子小,从前,很少有人在自己的房间,一家人住在一个小房间里是常有的是,今天仍然有人过着这样的生活。 在仅有的一个房间哩,如果要摆下全家人的床铺,就不能在那里吃饭了。这一点,褥子很方便。早晨,不需要褥子的时候,可以收起来。在没有了褥子的房间放上桌子,当作饭厅吃早饭。来客人的话,就在那里喝茶;孩子放学回到家里,那房间就成了书房。而后,傍晚又成为饭厅。然后收起桌子,铺上褥子,又成为了全家人睡觉的地方。 如果是床铺的话,除了睡觉的房间,还需要吃饭的房间和书房等,但如果使用褥子,一个房间就可以有各种用途。 据说从前,在纽约等大都市的大学学习的学生也租得起很大的房间。但现在房租太贵,租不起了。只能住更便宜、更小的房间。因此,似乎开始使用睡觉时作床,白天折小能成为椅子的、方便的褥子。

新视野大学英语第一册Unit 1课文翻译

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