Volume IX, Dec. 2012.
Journal of Environmental Studies [JES]
An International Journal edited by Community Service and Environmental Development Sector, Sohag University [SU]. Sohag University Publication
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[email protected]
Journal of Environmental Studies An International Journal edited by Community Service and Environmental Development Sector, Sohag University [SU].
Volume IX, Dec. 2012.
Volume content Mohammed J. Ali Al-atabi, 2012. Removal of Lead Ions From Industrial Waste Water. Journal of Environmental Studies, JES, Vol., IX: 1-7. Makarim M. B. Younus, Mohammed Al- Hamdany, Sahar Na'eem, Iman Abbas, Nabeel Noori, Hayder Shaghi and Ayad Hasan, 2012. QStudy of Cotton lints Discoloration Phenomenon and its Relation with Seedling Emergence. Journal of Environmental Studies, JES, Vol., IX: 9-14. Makarim M.B.Younus, Hasan Y. Jabir Nabeel N. M. Ali, Ayad H. Kadhim, Hasan A.W.Abbas, Sahar N. Abed- Alwahab, Abed Al-kareem M. Taki, Kifaya A.Atiyah, 2012. Detection of pathological changes in Tilletia spp. The causal agent of covered smut (Bunt) disease in Iraq. Journal of Environmental Studies, JES, Vol., IX: 15-19. Faiza Ez. Gharib, Talib A. Al-Sarify, Ali F. Atshan, Zainab Talib Al-Sharify, Muna Abed Jaffar, 2012. Improve Thermal Insulation And Physical Properties of The Iraqi Plaster Using Natural Additives. Journal of Environmental Studies, JES, Vol., IX: 2128. Hassanein A. M., Galal E., Soltan D., Abed-Elsaboor K., Saad G. K., Gaboor G. M., El-Mogy N. S., 2012. Germination of jojoba (Simmondsia chinensis L) seeds under the influence of several conditions. Journal of Environmental Studies, JES, Vol., IX: 29-35. Waleed M. Sh. Alabdraba, Afaf J. Obed, Masuod M. Hazaa, Safa Badeaa and Manolea Aiden, 2012. Comparison Between Continuous and Batch Flow Activated Sludge Reactor to Remove Nitrate and Phosphate From Domestic Wastewater. Journal of Environmental Studies, JES, Vol., IX: 37-42. Ali Salim Joodi, 2012. Modeling of the heating transfer in the karst aquifers for Val d'Orléans city (France). Journal of Environmental Studies, JES, Vol., IX: 43-51. Sadiq Salman Muhsun, 2012. Characteristics of the Hydraulic Jump in Trapezoidal Channel Section. Journal of Environmental Studies, JES, Vol., IX: 53-63. A. A. El-Khatib, D. E. M. Radwan, A. A. Alramah-Said, 2012. Morpho-Anatomical Characteristics of Olive (Olea europaea L.) Trees Leaf as Bio-indicator of Cement Dust Air Pollution in Libya. Journal of Environmental Studies, JES, Vol., IX: 65-72. Mohammad Abed Abu-qulah, 2012. Following characteristics of knowledge management to achieve quality assurance of higher education. Journal of Environmental Studies, JES, Vol., IX: 73-81.
Journal of Environmental Studies [JES] 2012. 9: 1-7
Original Paper
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ا ? إزا ا=< ،tAوز&دة G3ر; ا"*ء و> K دة O>9ا" +ور+ P3ى أداء أYء هO+N ا"+ر& وا" 3; ،O3 Kإ" 5ر P3آK Q ا"!ت ا" R1ا"=> G+م Oو 9ا"+Mت ا" W t W+& ،Oا) > hOJ GJ1إدارة ا" K B" " 3أهB G3ا" Aت B 3J> dLو. B" Bو KA& ،B AI lا"را ) Nا"-: "+ -١ه 7ه5ك =; 89ا ,ا < ; :ا>: ا'ر@? )أ!اد ا! ( ون دة ا ! ا$ت ا*رد& ا +,؟ و@ = HI5هGا ا?Fال ا? ا*ول ا*)> ا /ا- : K ) (١-١هHIJ " Qت ا" ا"LMJ> G+ه ا" NOا"+ر& )أ3اد ا"; G3 * ( 3ن دة ا" G3 +ا" Aت ا)رد Cا"! ؟ ) (١-٢ه1!" Qة Yه Nا"+ر& * ; G3ن دة ا" G3 +ا" Aت ا)رد Cا"! ؟ )(١-٣هVC +& Qم إدارة ; X1ا"Mدة G3ا" Aت ا"! ا)رد C؟ ) (١-٤ه; & +& Qن ا"Mدة؟ -٢ه 7ه5ك ا %5Iا 5$ا(ت ون دة ا ! ا$ت ا*رد& ا +,؟ و@HI5 = هGا ا?Fال ا? ا &Hا*)> ا /ا : ) (٢-١ه 1" Qو> P&Jا" 1+Aا; 5 6ن دة ا" A " +ت ا)رد Cا"! ؟ ) (٢-٢ه Q " Qا" "JA+ا"& Rا; G3 6ن دة ا" A " +ت ا)رد Cا"! ؟ أه'اف ا'را) وأه:: >]> Gأه ه dmا"را إ" 5أن 6ا>Mهت L+ا&ة G3 ا"Iآت G3 9ا"[+ة ا"" Q&> G3 QR+> ، أ" Oإ" 5أل 5 Bا" 3و>& Qا"Iآت إ"b 5آت 5 Bا" 3أو bآت 3 " B*9 آ" xت ا" cF ، +أ y 2+16ه dmا"Iآت
Journal of Environmental Studies [JES] 2012. 9: 73-81
FMCها G3إدار> ، 3 " Oوآ M+C 2Cه dmادارة ا"Mة ا"[+ق وا"=+م وا" P 3Jا"Iآت ا"1Aى G3 .O>DMوVCا " y B+==Fا" xت ا"1Aة K FMCت هة M+Cا"م وا" K 3ا" O&" K QAI> cFا"> W=C 3ل G3ا"VJت و 89 ا"R+ة .OJو" " K 3اه+ت "^VJ G3 Bت ا)ل وا"1+& G+ه ا" y1ا"1!" Rي ا"VJت G3ز&دة إ O++Cوا" K Q =+ا)W9ء و"=C Mط ا" zYإن وت. أه'اف ا'را) : ':ف ه NGا'را) إ ا*ه'اف ا -: - 1ن ا 789 6ا"; G3 3ن دة ا"G3 + ا" Aت ا)رد Cا"! +D ،د :5 أ 789 -أYء ا"NOت ا"+ر& ا" cF K ،O3ا"HIJت ا" ا"LMJ& G+وOC أYء ا" NOا"+ر& و19ا>. O ب 789 -ا" J1ا" "JA+" ++ا" ت Z > G3ا" Aت 1F cF K ،و> P&Jا" 1+A و ا" Qا" "JA+ا"&. R ج -ا 789 6ا"VC G3 3م ا"Mدة G3ا" Aت ا"! . د -ا 789 6ا"; & G3 3ن ا"Mدة. O> – ٢ف ا"را " !وج K BMا" +ت ا"Oد 3إ" };> 5أه إدارة ا". 3 }+3 - ٣ا"Mل أم ا" KJوا" G3 Kإدارات xت ا" +ا"" Gا)رد[ G3 3دة ا" x G3 +ت ا" +ا""G ا)رد. C !ت ا'را) : ; G3ء AIا"را وأK+;3 l > O+ N ر K+ K+و" B;3 QAر K+3 K+;3 B K+و 5ا" Jا"-:G"+ ا /ا? ا*و: * > D :H-1ذات د B"Dإ K 8Fا"!78 ا" O P++& G+أYء ا" NOا"+ر& )أ3اد ا" ( 3و ;ن دة ا" G3 +ا" Aت ا)رد Cا"! J +ى د(05.0 ≥ α) B"D و@/ع :5ا/ت ا /ا : ا /ا /ا*و: * > D :HO-1-2ذات د B"DإK 8F ا"HIJت ا" ا"LMJ> G+ه ا" NOا"+ر& و ;ن دة ا" +و& ;ن ا"Mدة G3ا" Aت ا)رد C ا"! + Jى د.(05.0 ≥ α) B"D ا /ا /ا: &H * > :H-1.3ذات د B"Dإ19 K 8Fة Y ه Nا"+ر& و ;ن دة ا" G3 +ا" Aت ا)رد C ا"! + Jى د(.05.0 ≥ α ) B"D ا /ا? ا: &H & D :HO-1.4ا 78!" 6ا" J1ا""JA+" ++ ا" ت ; 5ن دة ا" G3 +ا" Aت ا)رد C ا"! ، و/ع :5ا/ت ا /ا :
74
ا /ا /ا*و: & D :HO-1-2ا 1" 6و> P&Jا"5 1+A ;ن دة ا" G3 +ا" Aت ا)رد Cا"! . ا /ا /ا: &H Q " 6 & D :HO-2-2ا" "JA+ا"&5 R ;ن دة ا" +وا+د & ;ن ا"Mدة و>I "[ Oا".(Stromquist, 2000:3) X - ٢إدارة ا" : 3ه Gرة ا"[د 5ا)bء و>Lه B^8 B = G3 أو ا"=رة ا" OA +& G+ا"[د و&!OCL+ 9ا.(Wit Meyer 1998:76) B3 X -٣إدارة ا" : 3ه GC M Gو[ه و=+ات ا"[د B1I و>8رات ذه > K " BJؤDت B>FHو== Bإا> && " Bأن &M) B3ب، .(٢٠:٢٠٠٢ -٤إدارة ا" : 3ه Gا"=VJ" dت أل ا"م وا"[+ح "*AI Qت ا)ل ا"^) Yا"(٤٦:٢٠٠٢ ،G1 A -٥إدارة ا" : 3ه Gت Kا" KLوة " C1ت ا" JOوCذج " * +ت وا" ل ا"P Q+ " J ا"*AIت إ" tC 5ا" 3ا" VJ " 88!+ )ا"LJي(١٢٨:٢٠٠١، "= Fد ا"RF1ن 789 9دارة ا" 3وه-:G 8> -١غ = G3ل ا)3اد " ، M+و> M+C Q8 > + Oار. -٢إدارة ا"+I 3آ K Bآ 3ا"[Nت وا"+Mت ا Wا"!1ات ا"+Iآ . J; Q=J>-٣أو }& QAIأو BM Z +& P+M Kا" 3ا" وا" B3ا"!. 8 -٤أ+D &F OCار& إدارة و> &Wا"VJت وو O>Fو> t W+آ [ Bآ*" d1آ +ب و> }18أJ K6 > t +Aو Kا" OO3 t8و>و& OYو>= Oو O+C وا.O + J" ]O+> -٥ع K Kا)ل و 9) 3+> Dو&G^1J ا" PJ" O V3ا = K O9 J+ا"VJت وا[+Fظ ا" BVJرف أ " OYع إ"> J OآQ " O إدارة ا! : > GJدور ا"MC G3 3ح VJت ا)ل P ه Z > Q&> G3 O+ا"VJت إ" 5ا8+Dد ا""G ا" &Mا"mي ت &ف 8+د ا" ، 3وا"mي &xآ 5 رأس ا"ل ا"[Aي وا" 5 3ا"*9 K 3J+ل ا"=رات ا" K *Y3 ، &I1دوره ا" > G3ل ا"VJت إ"+M 5ت B3ا"> G+ث ا"^+ ا"mMري G3ا" P zA++" VJا" ^+ا" &O+N G3 P؛ و Kه JاآO[ &> t +م ا" 3أهcF ، 9 B أن [Oم ا" G3 3ا" م ا 5 Q+I& +DاF ا" K 9ا" Kأو آ*ه ،ا)ول I& ،إ" 5ا"M+رب ا" VJوا1+9ر ا"[;ت ا" I> G+إ"C 5ذج ; Bو>[ & O[" Bا" ،Xوآ 2Cأآ RاM>Dهت
Journal of Environmental Studies [JES] 2012. 9: 73-81
G3 bا" م ا +Dوا8+Dد& > Qإ" 5ا" M+ وا"1هن &W+" ،ا"* ا" K 11ا"^+ات وا"[Q8 &+" OJا ،O+"*=+أ ا" Q9ا"Q9 O3 ،GCR اRCDو" GMوا"+ر& ا"mي از ا"+ا K Q9ا"=ى أ O B+Dوا"mي &[ QYا"Fة 5ا"[،Q8 و&آ Lادارة 5ا" Q9ا)ول. و; Kا"O+ت ادار& 3ن هJك > G3 K&1وOت VCا" K88!+وا"+Aب &> G3ا"[Oم ا" " OC] (1998, 34ا" B3ا" JYو >19 K BJY+ات وأA3ر وOرات & O1 +Aا"[د وK ا" B3ا"Vه dا" K M>Jا" P Q[+ا" N1ا"!ر " . ) ,٢٠٠٨, MCص.(٥٩- ٥٨ أه ا! ! ا?)Fت-: Iز أه ا! ! ا?)Fت (= 9ل ( @: -١ار إICء ا" F G3 VJذا>5 b1 QAI +& B MFا" 3ا"3) F+ص اR+Dر_ ،وف ا" ق، ا"ض وا" 5 t Wا"M+Jت وا"!ت 1H ، ا" K 3Jورا> ، Oا"*ء ا"+ن و.( O>&l 3> -٢ا"& 3د ا"=ار ا)M" QRل ا"IJط ا" G " ، xا" O3 z_> G+أا" Oوارده ا"، F+ وذ"*9 K Zل ا" 3ا") +ا"Vوف ا8+Dد& ا" ،ا"D+ت ا"Mر& وا" ، +ا"J=+ت ا" ة وا".( + > -٣د Cا" 3ا" VJ+وادار& ا" F+ " ، VJو "3وآ[ءة >=م Bادارة 8> K هآ Oا" BVJ+وا"_[ و VCا" Qوا+9ر >=Jت ا)داء. -٤ا" 3ا"19 K 1 +Aات و>Mرب ا ،K&9وا"G+ > G3 6xارات إدة ا" AOوإدة ا" JOوlه K وDت ا" &W+وا" G3 K +أداء ا"VJت. t > -٥ا" 3ا" J=+وادار& ا"" F+ى ا"&&K دورا رزا G3إMCح ا" XW!+وا" ت ا +C وا" =& +وا"" وا" QR> G+ا"=ل ا" G3 Oا"Q اداري. +> -٦ج ا" VJإ" 5ا" 3ا"M+دة b1 G3ة ت ا+9ر و> 8وإ+Cج ا" Pوا"!ت و>&W ا"د .OJ اRدة ! (?)Fت ا ا: إن } W8ا"Mدة ه )س [Oم ا8+دي _O Jء 5ا" 3J+ا" GJ8وا" K G"JA+ا"ول ا" J8ا"O ، =+ف ا 1دة ا+Cج وآ =6 t ا" ق وا"+Iي ،و"+> G"+آ Lا"Mدة 5ا"[+ق وا+Dز " Jا" G3 h+Jأي Mل ،و"= >Jول ا"RF1ن G3درا>; Oع ا"Mدة و dICو" BMا"RAون، وهmا أدى إ"J> 5ع و>د ا"[&+ت ا"! mOا ا"[Oم، و Kأ[&> Obت ا"Mدة ه >& zا" Mا)& A " د ،dو " 23ا"" ا"+آ و ا1 W+ Oت (1999:507 Bonser,) .B+وف )J.M. (Juran,وز ،Bا"Mدة إ OCى * ا"h+J "*+ل .و 23ا"Mدة 5إ OCى ا"P =W ا"1 W+ت .أ ا"ا [ ا"و" =3 ISO 9000:2000 23ا"Mدة OC] :در > M 1ا"!78 75
ا"رو G3 6ا"1 W+" h+Jت ا" ،Qوف )-17 (Feignbaum, A.V. 1991ا"Mدة ]Q[> h>C :OC HIC 789ت ا" K KA& dت ا" Qور.B>1l :/( +5م اRدة: > Oد [Oم ا"Mدة إ Dأ G3 G=+ > OCأر J ر ،Bوه:G .١اRد :Nدر ا:7T/ M"3دة > V" GJا"Jس ا" ،QY[+إي >[5 B QY أ9ى. .٢اRدة :ا)9 ;Uل: >ف ا"Mدة ]) OCا"ا "*+ل( وذ") Zه ا"Mدة G3ا" 8+وا cF K B+CDا" L +ت ا"Yور& " G3ت ا"Q ا"Vه& وا") . JYا" GWواد.(٢٧٥ ٢٠٠٣ ،d (IUت IUاRدة ! اZ5ت ا : إن أه 1 W+ت > و.O=1W> G3 OC -٣ود أهاف د K B=+I ،dا+Fت ا"[Nت ا" 3O+و Gادارة وا" .O==+" K }J -٤ا" Kا" =Rو> 5 OMIأداء ا" Qو>=& ا" OJ L+دون ا" G3 Q9+اMCزا> OJ> 5+F Oا" =R G3ر أ" Oدون ار>Aب ا)W9ء. -٥ا+Dد آ Kا" z&!+وا"+ه،5[W8) t ا)8Cري(٢٠ :٢٠٠٢ ، !ا' IUاRدة ! ا ا: أن 3ا > G &W> -١ا"VJم اداري G3ا" M+C Mو;ح ا)دوار و>& ا" xو"ت. -٢اDر>=ء +ى ا"!ت ا" +ا"= " *Wب ا" 5 AJ> G+ا. O>8!b tC -٣ز&دة ا"[Aءة ا" +ور+ P3ى ا)داء "PM ا)آد& Kوادار&.K -٤ا"3ء 1 W+ت ا"*Wب وا" P+Mوا" 21ا" G وا" ل إ" 5ر;ه .
Journal of Environmental Studies [JES] 2012. 9: 73-81
K 3> -٥ا"[+ه وا"+ون وا"*ت ا C C ا" Kا" .K KA> - ٦إدارة ا" QF K Mا"*AIت "Wق ا" ا" 8وا"*9 K O Q+ل. ااءات ا" 8+وا" "F PJو.*1=+ O6 -٧ر+ P3ى ا"" Gى ا" 9 K K&[+ت ا" M *9 Kل إاز اL+"Dام VJم ا"Mدة. -٨ا"+ا Xوا" P K QA+ا)آد& Kوادار&G3 K ا" Mوا" Qوح ا"[&< ا"ا.F VC -٩م إدارة ا"Mدة ا" }J& Iا" Mا+Fا و>=&ا و ر dده BJا&.BM ) ٨٤- ٢٠٠٢:٨٣ ،Y9؛ م.(٦٧٧ :٢٠٠٥ ، (ا 7.دة ا: إن دة ا" =J> +إ" 5ة ا QFوه:G ا .ا*و F) :ا" :( =+و& O1 +ا"+ف 5ا"; Pا"= "-:cF K A اCAت ا"د& وا" &I1وا" =&Wا" O = Jا" ا". + ا .ا &W> F) : &Hو>VC B&&W> BW9 m[J [+D B bء 1 W+ت ا"Mدة *9 Kل إICء د"Q ا"Mدة وإاءا> .Oو> ت ا" Qو K BWW9اQ ;ن ا"8ل VC 5م ا"Mدة ا" Wب وذ"+" Zون G[_ Pا" Aو 6 Kا+د K dادارة ا" ا .اVC F) : HHم ا"Mدة( :و& + VCم ا"Mدة G3ا" Aت وأ Oا" و 5+FوFا>O ادار& وا"[ ، Jو>=م ا"Iآ ا"xه و Kو> ت VCم ا"Mدة. ا .اا; F) :إاد ا hواد ا"+ر&:(t G3 +& cFه dmا" Fإاد اد ا"+ر& tوا" + "! z +ا" &+ت ادار& *9ل +3ة > ر& G1 +J K BM tا"VC 5 Aم ا"Mدة )ا)&Lو (٩٠٠٢ :و> B>=1Wو&=م هDxء m[J+ا"+ر&t =1" =FDا" Kو&آ Lا"+ر& 5 tا" =&Wا"5 R اء ا"ا ا"ا. 9 ا .ا?د) F) :ا"ا ا"!ر ( 2F :أن ا" OMا"OI " Cدة >=م "ا Kا + Q ا[+ء VCم ا"Mدة "1 W+ت ا"ا [ واآI+ف DFت م ا" =Wوا>!ذ ااءات ا" 8+وا" "".O+M ا %.ا?; F) :%ا" :(79+وا" +> G+إ>م ا"ا ا"!ر Kا" OMا"OI " Cدة & +ا>!ذ ا"=ار Iن Ob }Jدة ا"Mدة ا"" )ا)&Lو G3 (٩٠٠٢ ا"" ا" " +ا [ 1) .ا"(٦٥ ،٢٠٠٤ ،KF ا'را)ت ا?; : ا'را)ت ا; : -١درا )أ ،B1ه J .(٢٨,٢٠٠٤ ،1ان ى > Z > ا 3و_ zإدارة ا" 3وأ6ه G3 3ا"&& G3 Kا"زارات ا)رد ، Cو ه 23ا"را إ" &W> 5إHرا [ه" Gأس ا"ل ا"[Aي و G3 B>CAا"Mت ،وآZ"m > &Wأدا K B=+" dا B Qو> b إدار> ،Bو> 2ا"را إ" 5ا"& Kا"، h+J أزه أن هJك * Hد& K Bا"QAI + م وا)داء ا8+Dدي أو ا. +C -٣م )ا" (٢٠٥، ١٩٩٧ ،Gرا Jان ادارة "J> ، 3و"L 2ات 8ا" 3 وا" ت1+ ،ر dا"آLة ا) J G3ء ا8+Dد ا"،GJHآ> Z"mث Kا=+CDل إ"5 8ا". 3 -٤درا )ا" ا" (٧٨,٢٠٠١ ،GCإدارة ا"" 3 وا" G+ه 23إ" 5ا"+ف 1H 5ا" 3 ا" ، VJ+وأ ،O"Abوا ،O 9و28 9 Yورة > PMIت ا" +وا"1+دل ا"G3 KأYء ا" ، VJوأآت 5أه ا"8J ا"I1ي m[J> G3ا+ا>Mت إدارة ا"، 3 و> 2إ" 5أه ا"8ب وا"=1ت Fل إدارة ا". 3 -٥أى )ا"! (٤٦,١٩٩٦ ،GM3درا Jان"ا" Q9ا" Q > G3 G3ا+9Dر ا+Dا> :GMدرا ا+9ر& J G3 Bا"K+ ا"ا " ه 23إ" 5أن هJك *Yت B&A3 B&VCو> K B=1Wأه_ Q > Oه>G ا" 3ا" VJ+وا+9Dر ا+Dا>GM و>[ ه. -٦درا أاه ا"LJي G ،و "} )J (٢٠٠٨,٢٦٨ان" إدارة رأس ا"ل ا"[Aي VJ G3ت ا)ل" cFأآ أن " 3 GO3 .789وا"mآء &ان ا"دان +ز G3أ& VJأل ،و&6xان G3ا)داء ا""G وا" VJ " G Aوه ا"اد ا"!م " BM+JC و ،B1Cوا"= ا"== " Q=C G3 KA> VJ ا" 3إ" 5وا ،Pو>=< أداء [+ق ورd >.B 3J ا'را)ت ا*I5 -١درا ) ،(Laszlo, 2002,66و ه23 ا"را إ" 6*6 };> 5أل ت Oإدارة ا" ، 3وه Gا" QMا)ول cF :رآ5 L ه ا" 3وإدار>*9 K Oل اآ +ب ا"mآء ا" "JA> G3 QR+رأس ا"ل ا"[Aي ،أ ا" QMا" :GCRرآ 5 Lا"د Kإدارة ا"+D 3اح A+ن *9 K Bل ت ا" +واA+Dر ود هmا ا" QMا"VJت ا" +و KAا" Kوا"Mت Kااع وا" C B+ا" QMا" c"Rا"mي رآ5 L
Journal of Environmental Studies [JES] 2012. 9: 73-81
اIA+ف ا" +" Q1=+آ G^1J& 5 Lأن >Aن Bإدارة ا". 3 -٢درا ) ،(Mathotra. 2003,91و ه23 ا"را إ" 5و; Pم و>& & 1J "=س ا) ل ا" ، 3وJء Cذج B 1Jوآ Z"mآ[ > &Wرات وإCAت ا"=Wع ا"م G3هmا ا"Mل 2=1H cF ،هdm ا"را G3ا"&Dت ا"+ة آLMء IC Kط ا) ا"+ة G3ا"HIJت ا +Dوا" . -٣م )(1998, 134 Brain&Newman, را Fل "Cذج إدارة ا" ،" 3و G3هdm ا"را ا+ض ا" cF1ا" ا" "QR هmا ا"Jذج +د ا"ا zوا)د ،وbد ا" 5 cF1أه دور Fة ا" ، 3وا" J ا"6xة وا+ده آ O 8Jودا G3 Cذ.B G3 -٤درا ) Mentzer & Mastunol, 2000, > (26إاء ه dmا"را & K BJ 5ي ا"b G3 zJ8ا" 3إ"BJ; 5 & O P++ا)3اد أو 3ق ا" ،Qو>1ز G3 ا"[Aءة ا" l QAI ، 8!Iر ،Gو 5 ا" VJأن >.O 3 -٦درا ) zJ (Taylor, 2000:2ا" 3أOC _ه dو; BJو& KAأن >Aن = > Y >[ Q +" G11ا"=م ث ،KوBW >=م 5ا" M+دون >[ ا"ث ا\[ر ا 'را) : >J+ول ا"را ا" MOJ z&+ا"را وإاءا>،O hOJ J& cFو P+Mو Jوأداة ا"را ،وض ا" h+Jو 6 Kا" +ت. ( R:5ا'را) : "= ا!+م ا" cF1ا" hOJا" [ Gوا"MCD G +ز هdm ا"را ،و ا+ت ا"را ا" hOJا" [*9 K Gل ا*HDع 5ا"ا Pوا"رات ا)9ى ذات ا" ، 8أ cF Kا" hOJا" =3 G +ا> 21ا"را ا" } ا"اGC وا 2!+أداة ا PM" C1+Dا" ت Kأ3اد ا" J و> L> Oه. ( K61ا789 6 ا" J1ا" "JA+" ++ا" ت ; 5ن دة ا" ، +وآ Z"mدر ا"=+رب او ا"CM+ G3إت هDxء ا" ! K61ا"[; ا" . -٤ا1+9ر *" Reliabiltyت ا"1Rت "1رات ا)داة. '+ق أداة ا'را) و::I " ف 5ق =& أداة ا"را م ا"cF1 ض ا"1رات ا"^+ O+JY> G+ات ا"را 5 K BMأYء ه Nا"+ر& "Mت ا)رد، C وآ K BM 5 Z"mا"ر Kا" ،K88!+و >
Journal of Environmental Studies [JES] 2012. 9: 73-81
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ض &_ ا'را) : & KY+هmا ا"[ h+J " ; Q8ا" 2 > G+إ"O ا"را *9 Kل ا > Kؤ ،O>Dوا1+9ر O>;3و 5ا" Jا)>-:G ا /ا? ا*و: * >D :HO-1ذات د B"Dإ K 8Fا"!78 ا" O P++& G+أYء ا" NOا"+ر& )أ3اد ا"( 3 و;ن ا"Mدة G3ا" Aت ا)رد Cا"! + Jى د(٠.٠٥ ≥α ) B"D و@/ع :5ا/ت ا /ا : ا /ا /ا*و: * > D :HO-1-1ذات د B"DإK 8F ا"HIJت ا" ا"LMJ> G+ه ا" NOا"+ر& و ;ن دة ا" G3 +ا" Aت ا)رد Cا"! + Jى +ى د.(٠.٠٥ ≥α ) B"D " Kه dmا"[; > ا!+ام > Qا" K&1+ا)Fدي ) ،( Anovaوآ ه ;} G3ا"Mول ر ).(١ :fا?;
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"HIJ " ^+ت ا" . *9 K F*Cل ا"Mول ر ) (١أ* ،dأن ف ا" ) (٩.٧٨٦وه Gاآ B K 1ف ا"Mو" ا" ،(٣.٨٩) ^"1و +ى د (٠.٠٠٠) B"Dوه GاK Q ) t& ،(٠.٠٥ر y3ا"[; ا" و1ل ا"[; ا" &1وا" 5 7J> G+ود * ذات دB"D إ K 8Fا"HIJت ا" ا"LMJ> G+ه ا" NO ا"+ر& و ;ن دة ا" G3 +ا" Aت ا)رد C ا"! . ا /ا /ا: &H * > Dذات د B"Dإ19 K 8Fة ا" NO ا"+ر& و;ن دة ا" G3 +ا" Aت ا)رد C ا"! + Jى د.( ٠.٠٥ ≥α ) B"D " Kه dmا"[; > ا!+ام > Qا" K&1+ا)Fدي ) ،( Anovaوآ ه ;} G3ا"Mول ر ):(٣ +ى ا" "D :fا"Mو"B :f ا"[; ا0.05 K Q ا" ا)و"5 ٠.٠٤٩ ٣.٨٩ ٣.٢١٦ H2 ا'Rول ر Q > h+C .(٣) 8ا" K&1+ا)Fدي )^+" (Anova " HIJت ا" .
*9 K F*Cل ا"Mول ر ) (٣أ* ،dأن ف ا" ) (٣.٢١٦وه Gاآ B K 1ف ا"Mو" ا" ^"1 ) ،(٣.٨٩و +ى د (٠.٠٤٩) B"Dوه Gا،(٠.٠٥) K Q & tر y3ا"[; ا" و1ل ا"[; ا" &1 وا" 5 7J> G+ود * ذات د B"DإK 8F 19ة ا" NOا"+ر& و;ن دة ا" G3 +ا" Aت ا)رد Cا"! . ا %/ا? %ا:%&H & D :HO -2ا 78!" 6ا" J1ا""JA+" ++ ا" ت ; 5ن دة ا" +و>VC ،(٤–١إ&Mد ا"W+ت ا" واCDا3ت ا"ر& وا"> tودرت ا"ر )3اد Jا"را G3ا" Aت وآ ه ;} G3ا"Mول ر ).(٤
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*9 K F*Cل ا"Mول ر ) (٤أ* ،dن أ3اد J ا"را &ون ن هJك * 1F Kو> P&Jا" 1+A G3ا" Aو;ن دة ا" G3 +ا" Aت ا)رد C ا"! p cF ،ا" X+ا" Gا"م " dmOا"[; ) (٤.٠٣٠٤٧٥ور ر "F cF ،Bزت ا"[=ة ر ) 5 (٢ا"> 1ا)و" 5ور ر "،B وا" 1F > "5 7J> G+ا"1+Aت G3ا+ب Pا"ا Pوا"ور&ت "F KF G3 ،زت ا"[=ة )(٤ 5ا"> 1ا)9ة ور ر " ،Bوا"28C G+ 1F > "5ا"1+Aت و> G3 O&Jا"8ل 5 ا" " ،وآ=3 P 2Cات ا"[; أ1ب ا"
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و;ن دة ا" G3 +ا" Aت ا)رد Cا"! . ا" &1ا" 5 7J> G+ود * Kا"Q *9 K F*Cل ا"Mول ر ) (٥أ* ،dن أ3اد J ا" "JA+ا"& Rو ;ن دة ا" G3 +ا" Aت ا"را &ون ن هJك * Kا" Qا" "JA+ ا)رد Cا"! . ا"& Rو;ن دة ا" G3 +ا" Aت ا)رد Cا"! ، p cFا" X+ا" Gا"م " dmOا"[; ا _5وا+ت: ) (٣.٨٨٤١٥ور ر "F cF ،Bزت ا"[=ة أو ً :eا_5 2 > –١ا"را إ" 5ود * ذات د "Dإ 8F ر ) 5 (١ا"> 1ا)و" 5ور ر ",B Kا"HIJت ا" ا"LMJ> G+ه ا" NOا"+ر& و وا" 3> "5 7J> G+ا" Aا" Qا" "JA+ا"& R ;ن دة ا" G3 +ا" Aت ا)رد Cا"! و +ى " F G3 ،" +زت ا"[=ة ) 5 (٤ا"> 1ا)9ة د.(٠.٠٠٠) "D ور ر " ,Bوا" 3> " 5 28C G+ا" A آ 3ا" L +ت ا"*ز ا"& ،" Rوآ=3 P 2Cات ا"[; أ1ب " y3ا"[; ا" و1ل ا"[; 79
Journal of Environmental Studies [JES] 2012. 9: 73-81
–٢آ > 2ا"را ود * ذات د "Dإ 8F 19 Kة ا" NOا"+ر& G3و;ن دة ا"G3 + ا" Aت ا)رد Cا"! و +ى د.(٠.٠٠٠) "D –٣و> 2ا"را إ" 5ود ا 1" 6و>P&J ا"; 5 1+Aن دة ا" G3 +ا" Aت ا)رد C ا"! . –٤آ > 2ا"را إ" 5ود اQ " 6 ا" "JA+ا"&; 5 Rن دة ا" G3 +ا" Aت ا)رد Cا"! m+ -٥ا'را) إ 'م Z& IUم اRدة ! ا$ت ا*رد& m+ -٦ا'را) إ 'م اد (@ &Zم اRدة ا'ة (= وزارة ا ا & :ا+ت G > –١ا"را Yورة أن >=م ا" Aا" ا"*زم " HIJت ا" " NOا"+ر& وذ"IC L[+" Z ا"1ث و>]" zا" t+Aوا"Iرآ G3ا">xات ا" .
–٢آ > Gا"را Yورة أن > Kا" AأYء ا" NOا"+ر& أ ب ا"!1ات ا"" وذ"[ " Zظ 5دة ا". + –٣آ > Gا"را Yورة أن >Lز ا" 1F A ا" 1+Aو> K O" " O&Jا G3 6دة ا"K + *9ل ز&دة ا"1ث ا" وا+ب ا") 1+Aآ 1آB Kا"ا Pوا"ور&ت و> PMIا"ر Kوا" 1 W "&Lر> Oو> QOا"8ل 5ا" .[+ " B -٤آ و> Gا"را Yورة أن > 3ا" Aآ 3 ا" Qا" "JA+ا"& K O" " Rا G3 6دة ا"*9 K +ل > 3دورات >ر& 88!+ B1واآ 1 ا"ا G3 6أ" tا" +و> 3آ 3ا" L +ت ا" ا"& Rا"*ز . G > -٥ا"را Yورة >VC -٦ا"را Yورة > & G3 O&J ا+ب Pا"ا Pوا"ور&ت > 1F PMIا"1+Aت و>O&J ا"ر Kوا" 5 1 Wز&ر>O > 1Fا"1+Aت و>G3 O&J ا"8ل 5ا" > 3ا" Aا" Qا" "JA+ ا"& + " R > 3ا" Aدورات >ر& G3 1آ 3 ا"DMت ا" 88!+ >اآ tا" Aا"ا G3 6أ"t ا" +ا"W+رة > 3ا" Aآ 3ا" L +ت ا" ا"& R > 5J1+ا"VC Aم ; X1ا"Mدة
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> :٣٩٤ز. م ،زآ& " .(٢٠٠٤) ،ى إدراك أه إدارة ا" 3ا" G3 1ا"Iآت ا" J8 ا" ه ا" ا)رد ،" Cر" + IJ lرة ،ا" Mا)رد. C ا" ،GWر ؛ ادة " .(٢٠٠٣) ،5 ،إدارة ا"Mدة ا"O[ : Iم وإHر " G3 K &+ت ا)داء " >x ،آ ا8+Dد وا" م ادار& ا" ،GCRا"Lرء ا)ه ،ا)ردن. 1ا"" .(٢٠٠٤) ، ،KFا"Jه hا"+ر& ا" hOJ : A+إدارة ا"Mدة ا"QIة " ،آL
Journal of Environmental Studies [JES] 2012. 9: 73-81
Wiig, karl M. (2003, 76). "Knowledge Management Founation : Thinking sike, B. & Alan, F. (2000, 87). "The transfer of knowledge & The Retenation of Expertise: the continuing for globel assignments,journal of knowledge mgt V. (4) N (2) Stomquist, n. & Samoff, j. (2000, 3). knowledge of management system journal of comparative education, V. (30) issue (3) Taylor, R. (2000, 2). "KM" The management Process of Ensuring The Organizations Existing Knowlewdge assets Johnson, G. & Scholes, K. (1997, 34). "Exploring Corporate Strategy"4th ed., Prentice-Hall,Europe &و$e< ا8اا Cا)رد G""ا +"ا وزارة P www.mohe.gov.jo
1W" ا،( PMEC) "دارةJO"ات ا1!"ا . " ا8 &رO ، ا"=هة، CR"ا إدارةz_ و3 " ى >ا.(٢٠٠٦) ، ز&د، CرW="ا G3 K&&" ا3 G3 ه6 وأ3"ا l + " ر،" Cا"زارات ا)رد . ا)ردن، >x ،رةIJ hC " .(٢٠٠٢) ، ،ري8C) ا،F ا،5[W8 لM" اG3 O>=1W> وI"دة اM"إدارة ا t&ر+ " G" اL ا"آ،W ،" ي+"ا .h !"ي "ول ا+"ا ا"[ه: 3"( "إدارة ا٢٠٠٨) ،د1 MC ، MC IJ " دار ا"راق،" ت وا" تM>ا+Dوا . ا)ردن، ن, CR" ا1W" ا،P&ز+"وا إدارة رأس ا"ل،٢٠٠٨ }" وG ،يLJ"ا ت ا)لVJ G3 يA["ا I5* اا< ا-ب Bonser, C. (1999,36). "Total Quality Education " ،Public administration Review, No. 52. Laszlo, A-Laszlo, K. (2002, 66). " Evolving Knwledge for Development :The Role of Knowledge Management in Changing World". (JKM vol. 6).
Abstract
Following characteristics of knowledge management to achieve quality assurance of higher education Mohammad Abed Abu-qulah
The study aimed to know the effect of following some of the characteristics of knowledge to achieve the quality assurance of education "study applied to private Jordan colleges," The study indicated, there is significant statistical relationship between the activities carried out by faculty staff members and ensure the quality of education. In addition, the study indicated that a trace of computing, diversification of the library contents and provide the means of modern technology are important to ensure the quality of education. The study provided a set of recommendations, including the college offers support for the scientific activities of the faculty, and to appoint members of the owners of high expertise, and enhance and diversify the computerization of the library, and provide the necessary technological means for education.
81
Journal of Environmental Studies [JES] 2012. 9: 9-14
Original Paper
درا ه ة ن ات ور ا و"! وغ ادرات رم ،ا ا ا ، ،إ ن س ،ري% ،ر #$وأد &'% '-أاض ا+ت /آ 2 / 0و &' /ا+ت /دا5ة ا ث ا0را /2وزارة ا8م وا: ،6+7اد /ااق
إ'در M_* .(١٩٨١) . آ اY ء ا داود و: ا(مg*(N وA ااJ &ق ا ب4& ا.'-3 اD 43( ا4' اD& E ' را.' ا' ث اqP ي3ا .٦٢-٢:٥١ ،') -4ا &رم، ! " ،KN ا،اا ، رR !ل ا،$ BV ر، أد آ، اا س ، ري،ن-آ .(٢٠١١) .)* &اهب و ا iA ف3R | أM4 ' RZأط ا (4ت ت ض اI. \ 'A ا .ت )و' اضM أو رi\ و1$ا .٧-١ :(٢) ٢٩ ،' ' اA' اX ، إ اه#D ر3& أ، د د،اوف . و د ا ي3Xا س ا 3 (ات )و' ضL اث4 ا.(١٩٩٥) .e R "3h اX هD ' ادي-3ا -٢١٣ :٢٤ ،' را.' م اA' ااXا .٢١٩ . زآ' د، ر و4 ا،Xا ,$3 دار ا.i) أاض ا.(١٩٩٢) ٢١٥ ،' ا&' ا ' اد،اض .'(R Al-Baldawi, A.A. (1993). Occurrence and importance of wheat and barley diseases in Iraq. Pages 105-113 In: Proc. Workshop on the Technology Transfer in the Production of Cereals and Legumes, September 20-22, 1993, Mosul, Iraq. AL- Maroof, E.M., Faidh, F.A. and Queli. A.I. (2004). Efficiency of some fungicides in common bunt disease control in wheat. Page 329-336 In: Proc. 2nd Int. Conf. Of Development and the Environment in the Arab World, March, 23-25. Bonde, M.R., Prescott, J.M., Matsumoto, T.T. & Peterson, G.L. (1987). Possible dissemination of teliospores of Tilletia indica by the practice of burning wheat stubble. Phytopathology, 77: 639 (abstr.). Fischer, G.W. & Holton, C.S. (1943). Studies of the susceptibility of forage grasses to cereal smut fungi IV. Cross-inoculation experiments with Urocystis tritici, U. occulta and U. agropyri. Phytopathology, 33: 910-921. Gaudete, D.A. and Puchalski, B.L. (1989). Races of common bunt (Tilletia 18
Journal of Environmental Studies [JES] 2012. 9: 15-19
Varenitsa, E.T., Saakyan, l.Y., Mozgovoi, A.F., Kochetygov, G.V. and Gradskov. S.M. (1987). Using derivatives of the variety Zarya as donors of resistance to bunt. Lenina, 4: 3-5. Yarham, D. (1993). Soil borne spores as a source of inoculums for wheat bunt Plant Pathology. 42: 654-656.
Parlak, Y. (1981). Seed-borne pathogens on wheat (particularly smut). EPPO Bul. 11: 83- 86. Souza, E., Windes, J.M., Sunderman, D.W., Whitmore, J., Kruk, M. & Goates, B. (1995). Registration of ‘Bonneville’ hard red winter wheat. Crop Sci., 35: 1218-1219.
Abstract Detection of pathological changes in Tilletia spp. The causal agent of covered smut (Bunt) disease in Iraq Six isolates of Tilletia caries and T. foetida, the causal agents of wheat common bunt have been collected from six regions in Iraq and identified by their reaction to 10 differential wheat lines, each containing single bunt resistant gene. Diversity of the pathogen isolates was confirmed according to their reactions. BU6 from Al-Qayarah (Mosul) was the most virulent isolate which overcome all the resistant genes except Bt7and Bt10. The least virulent isolates were BU1 and BU4. Bt7 ، Bt10 genes stayed resistant to all the isolates and the infection didn’t exceed 10%, although the isolates were mixture of Tilletia tritici and Tilletia laevis, followed by Bt5 which was resistant to most of the isolates except for BU5 and BU6 which excelled this resistance. Key words: Common bunt of wheat. Iraqi isolates. Differential sets.
19
Journal of Environmental Studies [JES] 2012. 9: 21-28
Original Paper
' %ال ا#اري وااص ا اا ام ا ت ا ٣
ة ا ،١ز ،٢ن ن ،١ز ز !" ،١ا ي ١آ *1ا ،*/0ا *".ا') ،*+,-ب ا'& ،%ص.ب 9) ،١٤١٥٠اد ،اق. ٢آ *1ا;م ا *" ،*1/0اا ،ا' ،*+,-ص.ب 9) ،٤٦٠٣٦اد ،اق. ٣وزارة ا;م وا9) ،1 ;;?,اد ،اق.
ا@,/م ٣ :د;C ٢٠١١ ،'-ل٢٠١٢ ١٨ :
ا)(: GاFا " Eأآ Hا?;ارث ً;1Lا' Jو ,CاN ،Fا أO PQورً %1'+Gا'Rت وا';') Jاد "Tو"* .EFأ\[ ه YNا';اد "دة ا W1 ،X.ا UVF,/أ;Jاع " ا_;اح اT" *1+.و"* `' EFاT,Jaل اF `-ارة _ اء ا'eة ا_dى و " 0,'FاN ،b,ا ازدادت ا * Fإ! درا */آ;d 1-FG *11اص ا X.اا,' .Cز اX. اا *1?1J?1" X +h) Cو *1 *1 1ا;.دة )TJ -وة ا';اد ا_و *1ا') 0" `+ا;h+ر ا (*1+.وا*JT, ا';,رة ا,Jlج ? ،هك ) mا1-ت ا ,أدت إ! *Cا o1و Uدون إ *Lاh,/ا" oآ'" o?/'G *- h,/p % @" 1 o.ام آ'دة را)*T" *C ،و"0 _ o,دات ا ،م "Tو" *); o,و q '" Y'.G */دي إ! -dرة آ1ة " ا X.أVء ا'[ ) ،oو)q ,دي إ! زدة آ* اء ! 9, .ه YNا1-ت %GهNا ا WFاh,/ام إOت "\ت X +d 1-F,ا X.اا %G W1 .Cاh,/ام أ;Jاع ة " ا'\ت ا *11وا ,ه )ا،, ;Cر ازJ ،رة ا ،hا?ؤو (1و) *1" -ودرا" */ى 1VeGه YNا'\ت ! ا;hاص ا *1 1وا'*1?1J?1 X.اا ،Cإ *Oإ! درا -J 1VeG */ه YNا';اد ا'\* ! ا ل اFاري X.اا1,da Cر أ\[ "دة "\* "` اFظ ! ;دة ا'دة و)Tءه 'Oا';اQت ا *1/1Tا_ X.) *Qhاض اء XF %G .ا ل اFاري إ *Oا?ؤو ،1ا;C ،,ر از و Jرة ا hو) -ا;ز *h *-J % (١٥ ،١٠، ٥ ،٣) *1Jا_/س " ا X.وا'ء .و Cأ0wت ا VeG x ,ا ل اFاري )?[ آ *-) 1ا'ء إ! ا X.و); *1ا'دة ا'\* ) ،دة *-Jا'دة ا *11ا'\* *-Jإ! ا *hا_/س ا *1/1Tداد ا ل اFاري و 0wهNا وا ًFOاh,/ام Jرة ا hوا ,و ;Cر از ،أ" إ *Oا?ؤو oJy 1ا -ا G o" *1Tزدة ا ل اFاري أآ" H ا'\ت ا_dى وذ,' oJ_ zز )Tان "ء ا;,ر واNي ?[ G " %15 ً TGآ o"G o1ار ،إ aإ oJآ' زادت o,-Jإ! ا *hا_/س [Cا ل اFاري وذ;?G *C -) zن ا?* ا.*)a ا
+ت اا :ا X.اا ،Cا ل اFاري XF ،ا9\Jaط ،ا;C ،,ر ازJ ،رة ا ،hا?ؤو.1 ا :,- إ-Jن وادي اا أCم " إh,/م ا;h+ر ا *1+.و ا " ! X.ا;+ر );L *aا Xdا+وح ا\Fر* ا' " ! *C,ا;+ر ،أ" ا;Tد ا_1dة b\G Tا,Jlج '@d " ً 1ل )ء ا' `J+و1-FG إ 0,1 ,Jوا.," UVF,/ت ة أآ;G Hرًا ) ،%/ .(٢٠٠٠ا" X.آ آ'1وي ;?,ن " " " xة ";اد;?, W1 ،ن );+رة ر " *1-1آ,ت ا?;1-م، ; ا X.ااق )?[ /Gت وا */أFJء آ1Hة " ااق " ,Tدي وا?/lر* وا_راO ا;ا '01) *Cو " " *C," Eااق[0- '" ، ً 1F" o1+Gو)? .*\h" bإن "دة ا;+) ['G X.رة *11آ'&;"* رش "Tو"* EFذa zن ا;,F X.ي ! ;ا " %٢١ا'ء ا' 'O F,ا,آ 1ا;ري إذ F,ر آhر E1و dqاT,Jل اFارة .ا X.ا'+, " ,ض ) [F, EFر ت ارة )٢٠٠-١٠٠ 1 در * " *1d) *;Rوdون .(٢٠٠٢ ،إن إى أه% ا'.,ت ا *1+.ه " 0" [',-آ;eاح ز* Fارة ) ;') odاد ز* *11أو آ'1و* o,1"-" " G و [" `Gا ل اFاري W1 ،و أن إ *Oا';اد ا *1Gذات ا_1ف ا;1-ز* آرة ا G hا ل 21
* Corresponding author: Dr. Zainab Talib Al-Sharify
[email protected]
اFاري وا; G;+اح ا *1d) *1+.وdون، .(٢٠٠٠ ا_1ف ا;," *11ة "& %ا_Cر ا" *1و,FGج إ! در * " *1Cا'T" *.ر J `" *Jا %.Fأو ا;زن '& %ا_1ف ا * Nا yن آ* " ,G 0,.ا+,Cد*. إن اh,/ام ا_1ف ا `" *11ا X.و)Ceر 19Qة و," 1ا)* و" "+در ";" *,hز* )?[ ;ا ا'دة ا' *h *Rا;G ! [' X.ز` ا0 lدات، T" Gو"* ا ،ET,زدة "Tو"* ا [+وا_'ل ا -F ،*1 .ا'و+,"a *Jص ا;+) *Cرة أ\[ و " ;dاص ا ل ا G;+واFاري ) ،%/ .(٢٠٠٠إن ا',ت ا_1 *1//ف ا *11 ا P1-, 0',/ا'دة اT" *1J/hو"* ، *1 ""[ ا'و;C ، *Jة ا,ا) "` ا P-ا',ك 'دة اV ،*1J/hت 1ا?[T" ،و"* ;' *1اد ا?'1و* ،زل F 1ارة .ه zأ;Jاع ة " ا_1ف ا *11ا ,ا U"h,/آ';اد *hh," P1-Gآ1eف ;ز ا ،0أ1ف ا -ال ،أ1ف "hت +Cا ،?-أ1ف ا 1hران ،أ1ف b/ا ،[1hأ1ف ا?,ن ،أ1ف اh و) mأ1ف ا\hوات U'G .درا */د آ;" " 1اد ا ل اFاري " ا_1ف ا *1Gآ hوا? xG ,
Journal of Environmental Studies [JES] 2012. 9: 21-28
;?Gن "Tو"* Fا Eوا"+,ص ا'ء ،ا 1اNي `+ " Fء ا .وh,-م ! [?Lأ;اح ا.ران ا, ,FGج إ! ل وh,-G Cم ! ;F-" [?Lق وآ zNا1 اh+ي اNي ;?,ن " ;Qف hQي "' وج "` `C 19Qة " ا" `" hدة *TQaإ *1,/وh,-Gم هYN ا'دة ل "hزن ا ,وا'ت وا;1ت ا*+1d )أده .(١٩٨٤ ،%أ1ف ا ,ه ;Jع " أ1ف ا_ب ا';,ة )?Hة "& %دول ا be,G ،%أ1ف ا" , أ* " ا_1ف اT) 1FG ,ت !'-G *1TأFء ا_و وا) ,ا;?, ،1;.G 0dن ا@9ف " *11 @d ة Xh,-G W1أ1ف ا " ,ه YNا .@hأن ا*T ا_@h,/a *1//ص أ1ف ا ,ه " أ_ب ا *1-إذ `TGاGت ا *.Oو )Gآزم ') '9Gء 'ة ;ا أر)* أ 0@d [F,G `1)/اTة Gرآ* ا_1ف G W1ع أ_1ف اT1-ن و و .') b.G %V [-9Gأن [?L ا_1ف ";?G T 19,ن " 0Tدا * أو " *1,-أو )\1و* ،وآ 19, zNا Tا'? " ,'1" ٤-١ و;?Gن ا_1ف );ل ,'1" ١.٥وا;زن ا; ; 0ا FQ) ٠.٦٩وdون;G .(١٩٨٩ ،د "Fوaت اh,/ام Jرة ا hآ'دة d 'Oت ا X.إ! " *Rم ،ًTGو Cو أن ا'دة اFو* ! ا;1-ز *J," " G ا ،X.و Cأ ;F) Uث ة ;ل ا',/ل Jرة ا hإ,Jج ا;T-ف ا''; * ،ا- 1,ت ا'رات ،أ;اح ا;-ح ا' 1T) *1واد '` ا;)* و;اح *1dا;زن [',-,إJء "-آ "*\h ا?* ) .(٢٠٠٠،%/ ت );Fث ودرا/ت ة m) 1-F,ا;hاص ا *1 1وا' *1?1J?1واFار* واh,/) X. *1G;+ام ا'\ت ا *11وا? *1 1'1ودرا1VeG */ه ! ;dاص ا *-/q' WF) 0" ،X.دوآ1-دس ١٩٦٩ */ "آ[ ا X.وا'.,ت ا *1+.ااق واE,G , ); *1ا';اد ا_و *1وق ا,Jlج ،و Tو إن زدة *-J ا'ء إ! ا X.ز" ا z/',وT" [Tو"* ا9\Jaط، Nا yن زدة ز" ا ) z/',دة *-Jا'ء إ! ا X. [ ! / 1VeG " o ' !O" 1ا'Tو"* وا;زن ا; ) G .(Doxiad, 1969ا'.,ت ا*"d *1+. ار ً Nا 0Jyزل اري ،1و)' إن ا;,F X.ي ! ""-ت دy *T1Cن oدورًا ه" ً %1&Gا;)* W1 ) U1ارا/ت اJ *HFهة ١٩٧٩ */إن اX. ' X,آ'h) " *1ر ا'ء ا;.ي " `GGاFارة ودر * ا;)* ;1د و@d " 0,Hل ا.ف و)zN دور "& *); %ا ;.أVء ا [+اFر)Jهة، .(١٩٧٩درس 1982 */ Malhortaا ل اFاري ';اد ا *1 Jlآ W1 m.و ا " oJا';اد از* ارً ،و دة oاFاري Cم )h,/ام "\ت ة X.آ?ؤو;C ،1ر از; ،[-/ ،ت ،ا،+T "hت h" ،*1Qت زرا *1آ_1ف ا [1hوادي، ا;+ف,ا;+ف اh+ي ) .(Malhorta, 1982درس ا"\ ١٩٨٣ */ Jإ"? *1Jإ,Jج آ*1d *1+ [, ا;زن ) دة *-Jا'ء إ! ا `" X.إ;C *Oر از 22
) " %٢٠ *-ا;زن آآم b1dا;زن ) ،*hوآUJ *-Jا'ء إ! ا; % ١.٢ X.اح ا *1+.ا'*"h,- آ;Tا` W1 ،ا U\hJا'Tو"* إ! *1d) ٢%"/UJ ١.٥٦ وdون .(١٩٨٣ ،اh,/م ";ن J ١٩٨٣ */رة ا hآ'\ف 1إ! ا X.و) -وز،١٠ ،٥) o1J " % (٢٠ ،١٥ا *&hا_/س.(Mohan,1983) . أ ى " 'Fو اس ١٩٨٨ */درا1-FG */ ;dاص ا X.ا;JHي ا';,ا " `Tو /و ;ب ااق ،و " @dل ا.,رب ا_و *1ا ,أ ! U هNا ا;ع " اe) X.ن *-Jا?,ت وا;hاص ا [H" *1 1ز" ا z/',و"Tو"* ا9\Jaط "*\h *Oy) "C zNا X.ا_و اTوة إX ) o1 أو;JV X :ي( )(٦٠:٤٠) ،(٧٠:٣٠) ،(٨٠:٢٠) - %وآ UJأ\[ ا (٧٠:٣٠) *-J x ,ا ,أU زدة *-Jا?,ت " %٣٤-٤٢وا;+Fل ! ز" ١٣-١٧ z/'Gد *T1Cو"Tو"* ا9\Jaط Gاو-٩.٤ " U ' .٢%"/UJ ١١.٢إن ;d 1-FGاص ا X.ا;JHي ) *Oyا X.ا_و 1ا+,Cدي ) -آ* [TJاX. " ا' `Tا1.ة إ! ""[ و /و ;ب ااق )" 'Fو dون .(١٩٨٨ ،أ ت *1dا"\ Jو /ا"-ا h" ً HF) ١٩٩٩ */ت ""[ ا و)["" T ا;,-"Hن W1اh,/م اآم ا %وا hإ,Jج ا? [,ا ،*1+.و;"Cا ) yاء Q;Fت "Tو"* ا9\Jaط ) *1dوC .(١٩٩٩ ،/م 1-F,) ٢٠٠٠ */ [1T "Tو"* ا@ت اhا *1J/ا' *T-اh" *Oy) +ت ;aذ* d *.GJ *11ا* ا `Tا;aذ* " ا'"[ ا *1 ,Jlوه; @) E1Gإ *Oا_1ف ا;aذ* ا *)lا * اh,/aام ا/1C 'O +1+d `+G ,ت وأ?Lل 9 *,)Vض 1-FGا ا;hاص ا'*1?1J?1 *J/hوإ,Jج 1e) *F-" *J/dف ;aذ* ;?Gن ا[C آ* " ا *J/hا *11ا * ) .(٢٠٠٠ ،[1Tاh,/م ا ٢٠٠٥ */ا 1وا ,وا1T,ت ا *1T, )ء دار T) *1?/ب " "* ا'; ،[Qوذ zدة ا ل اFاري ،و) 1LG ,ا@0,/ك ا *Cا?*1 )0 " @dل [1TGا',/ل ا; [ /ا' *1?1J?1وا *1+ ا *R,وا ,و 0@dا';,-ردة وا'?* ،و)F" ,و* ' ;?Gرة " `" ً 1R1) *1?,ا 1,ت ا-Jlن ا'*11 و" oG,ا *1', aوا+,Caد* W1 ،ان دة ا ل اFاري 'دة ا 1أًVا آً1ا m1hGة EG اFارة " اhرج إ! اا [dو)? .آ G zNآ*H "دة ا 1دورًا ه" ً ر` "Tو" o,اFار*q W1 ،دي إh,/ام ا 1ذات ا *-اFار* ا?1ة إ! زدة اbh, ا " "' ! Fدر ت اFارة ) *,)Vا;_ [dل ,ة "'?* ) ا.(٢٠٠٥ ، ٢٠٠٩ */إ *Oه أ1ن ا?ؤو 1إ! ا);ق ;d 1-F,اص ا);ق ا' a W1 1F" x,زدة ;Cة ا ['F,واhJض Jذ* ا);ق ا' x,وآ zNاhJض *-Jا"+,ص ا'ء واNي ,ا"[ ا -1ذو)ن ا_"@ح وآ ،0,آ' أن اh,/ام أ1ن ا?ؤو, a 1 إ *Oآ *1 bوذ) ً1F" Y;, zه .(٢٠٠٩ ،أ[',/
Journal of Environmental Studies [JES] 2012. 9: 21-28
@/م وهى ٢٠٠٩ */ا %Fا @,"aآX +d o و"' 1ات ار* وآ'1و* و" *1?1J?1وآ" o?'G *1 )0 ['FGا&وف ا' *11Fا W1 ،*1/Tا *R10) Y@',/آ[, " *,hا_)د ،إذ o,R10G %Gآ'دة أوE *R" *1 ' *1ا Fوا *)9إ! أ.م *1" *11و)ه '*1 وزن ا?' *1ا " *.Gه YNا_.م ا ،*11Fآ' *R10G %G ا'دة اا)* اG [',G ,آ ! 01ا?);ن وا10رو W1F) 1أ ) oJا'"* اFار* 0" bh, a 1ا?);ن إذ ,ا10رو ،1و)/1Tت وز*1" o1J *1' U'Gا hا' J.,و' *1ا? )\ 1" 9و" *1' %Vا;+F b1.,ل ! ا X +hا';)* ا %Fا )@/م وهى.(٢٠٠٩ ، إh,/م ا' (٢٠١٠) */ا U11ا Jlا''ـد اNي ,زل اري و bT/ G;Qوا.رانW1 ، إن ا" U11دة ,FG a *11ق و [,G aو`" 19,G a "ور ا " "; ;دة ا;hQ [?L ! *1ر )آ*1J وـ 1 1h-Gـت ا U11ر * ارة -٩٠٠) *1 ١٠٠٠در * "',G (*;Rد " 0'. bO ٢٠ -٤ ا_ *J;?" Qد آ " 1اات ا;0ا o1 '" *1 * *1Qdا ل اFاري وا G;+آ' أT a oJ أي *1Qd " *-Jا ل "` "ور ا " ً&Jا ?;" oJدة ،*11و [F, [)C 1أو اT" ،[,و"* اFا ـE وا O 1+F,ا1ان " 1,/إ! أر)` /ت a ;0 ١٢٨٠ْ!, 0+در * ") *;Rا'.(٢٠١٠ ، إن ا0ف ا_ " //هNا ا WFه; X +d 1-FG ا X.اا `" CاFظ ! ;دة ا'دة و)'O 0 T ",ت ود ا';اQت ا *1/1TاX.) *Qh _اض اء )h,/ام أ;Jاع " " *,hا'\ت ا *11ا';,ة " ً1Fو)? bوا *Rوا,ف ! أ\[ ;Jع " ،0إ *Oإ! درا 1VeG */ا';اد ا'\* ! إ"? *1JاT" *C ! 9,و"* ا0 a X.دات ا وo'FG ا' *); mhو [TJ *);Qا_;اح ا?1ة " oا, [',-Gآ;Tا` )ء ،إ *Oإ! q '" Y'.G */دي إ! -dرة ء آ o" 1ا.o',/ ا رب ا Experimental Work ت );Fث ودرا/ت ة "اآ ا;Fث وا".ت ;ل إ,Jج 1;Jت 1ة " اh,/) X.ام ا;h+ر ا *1+.ا' *'1وا'@ '* ,Jlج أ;Jاع "" *,h ا X.و *R10Gا';اد )' @ *T %ا,Jlج و"ا') o ) 01در * اFارة ،ا,رج ا ... ،1Fا( أو "*. "آh,/) oام ا'\ت ا *11ا';,ة " ً 1Fو)?* وا .*RهNا ا %G WFاh,/ام أ;Jاع " " *,hا'\ت ا *11آ ,وJرة ا hو;Cر از وا?ؤو1 ا';,ة " ،1Fو;G %Gز; 0ا ً 1ا' `Tا*1?'- ;d 1-F, X.اص ا X.ا ا `-ا.+, ا اد ا0و: ا ا:2 %Gاh,/ام ا X.ا ا'L " x,آ* ا 1Lا_ه،*1 %Gإ اء ا [1F,ا? - 1'1ا';ا *Qا *1/1Tاا*1C ر ٢٦ %Cوا'TرF) *Jود ",ت ا';ا *Qا *1/1Tر%C 23
٢٨وآ' ".) 1ول ١أد ،YJأ" ا;Fص ا*1 1 -ا';ا *Qا *1/1Tاا *1Cر ١٩٨٨ *- ٢٧ %Cآ' ";.) POول .٢ ا 3+ت
ا%4 2 ٥١.٤٤ ٣٩.٥٨ ٠.٠٨ ٣.٨٢ ١.٠٤ ١.٧٢ ٤.٣٢
6ود ا ا( ت ا -ر٢٨ 7 ٤٠ [Ta ٢٦.٧ [Ta ٠.٢٥ a ٩ ! a ٩ ! a
SO3 CaO MgO H2O3 R2O ا;ا SiO2 اTان )Fق در * ٢٣٠م :ول x ,J .١ا [1F,ا? X. 1'1ا و"Tر,') 0,Jت ا';ا *Qاا.*1C 3ع ا#
ا4 2
در * ا;"*
٢
ا;Tام ا/1T ز" اz/', "Tو"* ا9\Jaط ٢ %"/UJ ٢ " 1ا?%"/UJ - ;Cة ا@+دة
٥٥ ٥ ١١,٩
6ود ا ا( ت ا - ر٢٧ 7 aا'[h" ! T, ر%٥ ! ١٦ %C ٢٠-١٢ ٦ [TG a
٤ ٣
٢ [T a C aا%" ٥ ! *'H
:ول .٢ا;Fص ا X. *1 1ا و"Tر,') 0,Jت ا';ا *Qاا*1C
?3رة ا?> J %Gرة ا hوا ,ه رة ا'hت ا *1Gوا';,ة )'"[ ا.رة و" o,R10G %VوY1\FG ً1ا ;?1ن " ً 1dا;ا وا';اد ا?'1و*. ا %و ?ر از: %Gا " ,ا'? Gا را *1و') Y' %Gء 'ة ;م آ"[ oL %VإJء " P-و;0 o\Gاء وذz ;+Fل ! `" Gف آ;" oJدة ذات *1)C ا"+,ص ' *1ء ،و) YN0ا *-J [1TG ?' *Tا'ء ا'\ف إ! ا X.أVء ' *1ا ،hوJ [' %, اء );T *-ر از )ا;-س(. أ Cن ا +ؤو:% %Gاh,/ام أ1ن ا?ؤو 1ا " 0 ) *11ا'P- ا *T" ;;1.دو *&F" *hاJaر ;G W1 ، أ1ن ا?ؤو1ت ا/G *11ت )' *Tدو .*hإن أ1ن ا?ؤو 1أ1ن ر;?G *1);/ن ! 1 [?Lت 1T) *'Jس أ?1" ٢ " [Cون وGآ 01ا;ري " ا;ع ا-ا /ا' P-ذو اTت 0GJ;?" ،ا? *1 1'1ا_*1// ) H2O (14)% -و AL2O3 (39,5)%وSiO2 ).%(46,5
Journal of Environmental Studies [JES] 2012. 9: 21-28
' RSا-ا> وا ت %G ٢اh,/ام ;Cا * )";ا 1Lو "?ت( ر)U )?yم و [C U&Jاh,/aام ،و" *T) 0, G %G %V L) *1dة '` EQ@Gا';ذج "` ا Tو*;0/ إdا .oا;Tا ا' XF *"h,-ا9\Jaط ه ;Cا * أ)ده اا- (١٠×١٠×١٠) *1d ا';ا *Qا_"? .(ASTM C 472-84) *1أ" ا;Tا )ا';ا (1Lا' XF *"h,-اFJlء آUJ ))eد ) - %/ (٥٠×١٠×١٠ا';ا *Qاا*1C ر.١٩٨٨ *- ٢٧ %C ٣إن ' `1ا';اد اا *dاhت ;?Gن "e10ة و ه ة ;/ hاء آ X UJأو "ء dأو ا'\ت ا *-J FG %G W1 ،*11ا'ء إ! ا;+F X.ل ! ا;Tام ا *h /1Tا' *1 و `1'.اhت "` ا';اد ا'\* و?[ ا- - ا';ا *Qا *1/1Tاا *1Cر .٢٧ %Cإن ا'\ت ا,FG *11ج إ! ;dات '\ *1\FGن إ0J q,/دي دوره ا';ب ا *hو " Gا ل اFاري X.آ' ه; "; POا?[ *-) ١ رة ا .hأ" ) " o , *-ا'?G ا را') '9 *1ء 'ة */ ٢٤ا'ء و,ك ' b.1ة */ ٢٤أdى ،و" ;TJ %Vم )*Oy ا X.و -ا -ا' .*1إن ا ' " *9ا, ا'ء ه; [1T,ا"+,ص ا'ء أVء ' *1ا.+
ا;ز *-J %(١٥ ،١٠ ،٥ ،٣) *1Jإ! ا *hا' *1 ) Xو"ء(. ) ٤إآ',ل ' *1اL" hة Q *1' %,Gا*1. ا' *J;?,ا;Tا ا*&@" `" ،ًT-" 0,R10G %G , ;Gز` ا;+) *1.رة "-,و* ا) Tآ' ";PO ا?Laل ٥ ،٤ ،٣ ،٢أد .(YJإن ' *1ا +آUJ %,Gدً&J E Cا +G *-ا X.وآ@, zN ;+ل Tت ز* ," 1ا)* "` "اة '*1 اص أVء ا" %G .+ء ا Tأآ " HاaرGع ا';ب ور` ا ا ;+Fل ! و ;,-" oي ;,,زع ا0 lدات );+ر "-,و* أVء ا.XF *- ٥إ'.Jد ا X.و'` ;+ل [Gآ1) 1'1 "دة ا X.و ا %,G Tإزا* ا;Tا ) ٢٤ .*/
X *d .٢ K+Tو"ء "` إ *Oآؤو1
?3رة ا?>
?3 Fرة ا?> ء ة I ٢٤
K&Fا 2ا ا ء ا ري أو ا Jا +ر ء
X *d .٣ K+Tو"ء "` إ *Oا, ' QاJ 2ض اO#ل ?3 NIرة : ?, >?Mا&L
h" :١ K+Tا'1ت ا';)* J 1\F,رة اh
ا Uوا>O ) *R10Gا;Tا و *d *R10Gا X.وا'ء -ا- ا % @G !,ا 1,lت ا';)* " ا ل اFاري%,G ، ' *1ا hوء " ج ز , [)C 1آ[ و%, ا hوً `O; .ا ٥١٠٠ *1'?) X.ام \G %Vف إo1 آ' " *1ا'ء )'Tار ٢٠٠٠ام "` ا',/aار '*1 ا hا1وي أVء ' *1إ *Oا'ء '` وث @,?Gت * " ا X.وا ' ،J.," 1d ! [+Fإن ,ة *Oy) a ا;?G hن ) ٣-١ 1د .*T1Cأن ' *1ا %,G hأو ً ا'ء إ! ا;+F X.ل ! ا;Tام ا*h /1T ا' ،*1أ" * اh,/ام ا'\ت ا *11آ, " %,1ج ا `" ,ا;+) X.رة 1ة )ون إ *Oا'ء ' *-J.ا %V 1hاء ) *Oyا'ء Gر 1.وا hوً، %,G W1إ *Oا'\ت ا) *11ا;C ،,ر از، Jرة ا ،hا?ؤو Y ! *1 [? (1و)- 24
X *d .٤K+Tو"ء "` إJ *Oرة ا[?L ! h ";;Lر
X *d .٥ K+Tو"ء "` إ;C *Oر از ! ;L;" [?Lر
Journal of Environmental Studies [JES] 2012. 9: 21-28
ا 4, 3ا وا (#ت ا : #ا 2#30ء: 'J XF %Gذج ا X.ا1T *Qhس "Tو"* اFJaء 1,TJ load [' 1-G Eو;?Gن ا' *-ا*1+ ) 1ا' %/ ٤٠ -و %,ا %/ ٢٠ *-" ! [1'F, ا' -اNي * ا;',ج .%/ ٥وه YNا19,G %1T -ا XFاNي .1/ي ) %G T J-' *-إh,/ام إ;/اJت Qة ا'ن و);ل "-وي ض اT \'ن +Gف ه YNا;Tا آ''\ *1-) J-ن ;Gز` ا ! ['Fض ا;+) Tرة "-,و*. #ا J 3Zط: ?" XF %Gت ا X.ا1T) *Qhس "Tو"* ا9\Jaط ;C 1-G Eى ";Fر* "Lة ! P/ا';ذج );? W1Fن و 0ن "@)T,ن ا! ;Cى ا9\Jlط و %,إ اء XFا9\Jlط )h,/ام 0ز "Tو"* ا9\Jlط.
;'J .٨ K+Tذج اXF
.٩ K+Tا *1و 0Oدا [dا0.ز
;'J .٦ K+Tذج ' XF [HاFJaء
#ال ا#اري: %Gإ اء XFا ل اFاري 'ذج -ا';ا*Q اFاري ا ل )0.ز اا*1C ا*1/1T ThermoinsulatingواNي Q " be,وق d " [1,-أ)د o) `O;G %/ (١٠×١٠×٥٠) Yا;?G *1ن ! `)" [?Lو) %/ ٢.٥ z'-و"-ة " ا1J. ) 1G19Q 1,1d 1,Tو 0ز ) " oدوج اري );,-"Vن( د ٢ا_ول اف [Cا) *1إدdل( وا JHاف ) ا) *1إdاج( 1Tس ا) 19,ر * اFارة )آ' "; *FOا_?Lل ٧و ٨و ٩أد ،(YJوC Nde) 'Cة Cاءات *1ا;اة '@&* اق در * اFارة W1 ،أNdت أول Cاءة )ء ا; UCو" %V ;?Gن ا,ة ) 1آ[ Cاءة ١٥د.*T1C
0 .٧K+Tز XFا ل اFاري
25
ا 4 2وا :? 2 Ve,ا ل اFاري )?[ آ *-) 1ا'ء إ! اX. )ا;Tام ا (/1Tو *1;Jا'دة ا'\* و 0,-Jو)*T ا *R10G hا'ذج ،إذ إن ا دة *-Jا'ء إ! اqG X.دي إ! GاR .ت )\ 0ا mوGك ات ) hG 01ا'ء "' qدي إ! إhJض ا ل اFاريN ،ا .ا *-) %?F,ا'دة ا'\* @, هNا اhJlض .إن إ *Oا'ء إ! ا X.ا " b+ );F, (CaSo4. ½ H2Oل إ! Rت (CaSo4.2 ) *1 V P+, H2Oآ *,ا';ذج ',/l *.1,J *Qار* ;?Gن ا;رات ا *)lو W1 0?)Gداد ز" ا; ;) z/',د ا'دة ا'\* ) ،دة *-Jا'دة ا'\* داد ز" ا *-) z/',أآ _ [CG 0Jو;Qل ا'ء إ! ا;رات و ;?G dqGا?* ا;ر* ا ًQ;+d *)lإ*O ا?ؤو 1اhم [+1ز" ا X. z/',إ! ٢٨د.*T1C إ اء اام ا ا و ا ت #ادة ا و ا .آ)* )('& اام ا ا %٦٨.٥٥ا،1 و => :8ز;دة ) 2اء إ 3ا ا ا .أ :? #إ9 4داد 78إ6(#ص ا 'ء ) -ا *1)Tاh *1م ا?ؤو+,"l 1ص ا'ء. XF %Gا ل اFاري إ *Oا?ؤو ،1ا،, ;Cر از و Jرة ا hو) -ا;ز،١٠، ٥ ،٣) *1J *h *-J % (١٥ا_/س " ا X.وا'ء ،آ' "*1 ا_(١٧ ،١٦ ،١٥ ،١٤ ،١٣ ،١٢ ،١١ ، ١٠) [?L وا PO;G ,أن ) دة *-Jا'دة ا *11ا'\* أU زدة ا ل اFاري *-Jإ! ا *hا_/س ا*1/1T و 0wهNا وا ًFOاh,/ام Jرة ا hوا ,و ;Cر از ،أ" إ *Oا?ؤوy 1ن ) -ا*1T أ Uزدة ا ل اFاري أآ " Hا'\ت ا_dى )ا;C ،,ر از و Jرة ا,' oJ_ (hز )Tان "ء ا;,ر واNي ?[ G " %15 ًTGآo"G o1
Journal of Environmental Studies [JES] 2012. 9: 21-28
ار ،إ aإ oJآ' زادة o,-Jإ! ا *hا_/س [Cا ل اFاري وذ;?G *C -) zن ا?* ا ً' ،*)aإن ز" ا *h z/',ا_/س X.ه; ٥د E Cو إ *Oا?ؤو ٣ *-) 1و ! % ٥ا;,ا زاد ز" ا z/',إ! ١٥د ،*T1Cوإن ا'& 0اhر 1ت اX. ) إ *Oا?ؤو 1آ;) UJن ا) .m1و" ا*1 ا+,Caد* ن آ* ا X.ا' *Oy) -Fا?ؤوo1 1 زدة *1CوT" *1 ,Gر `" *Jا -F,ا';Fظ *1;Jا `1' X.ا;hاص. درا */و [1FGاQ;F x ,ت ا;d 1G ,اص ا ل اFاري إJ *Oرة ا hإ! *dاX. ; إن إJ *Oرة ا hإ! ا*1)C " X. oاFاري ،إ aإن زدة Jرة ا*1 -) h qدي إ! *1)C [1TGا X. [19,اFوي ! Jرة ا *1)C -) *1 -) hا"+,ص 'ء ) .دة ";,Fى Jرة ا hاqG X.دي إ! زدة ز" ا +,ا_ 0ن ه YNارة ;,FGي ! ا وا?-ت وا;1-ز وا? 1وا 1,وا! VqG , ' *1ا_"ه oو " Xh,هNا ا 1Ve,ا\ر e.Jإ! ا' *.ا' *T-رة ،أ" ز" ا +,ا,)aا [T oJy ); ;د ارة _ X,'G 0Jءًا " "ء ا .hإن زدة *-Jارة اqG X.دي إ! إhJض *1)Cا[19, "' qدي إ! زدة *-Jا'ء إ! ا;+F X.ل ! *1)Cا [19,ا';ب و? ذ;? zن ! -ب ا'Tو"* .إن "Tو"* ا9\Jaط X.اFوي ! Jرة ا;?G hن " *,إ! " *\hا',دا ! J *-Jرة اT" [TG W1 hو"* ا9\Jaط ) دة J *-Jرة ا .hإن ا X.اFوي ! Jرة ا;?G hن *1d ا;زن N0ا '? اh,/ا"_ 0اض ا ل ا.G;+
XF .١٤ K+Tا ل اFاري '\ت ا%٣ *-) *11
XF .١٠ K+Tا ل اFاري إJ *Oرة ا.h
XF .١٥ K+Tا ل اFاري '\ت ا%٥ *-) *11
XF .١١ K+Tا ل اFاري إ *Oا.,
XF .١٦ K+Tا ل اFاري '\ت ا.%١٠ *-) *11
26
XF .١٢ K+Tا ل اFاري إ *Oا?ؤو.1
XF .١٣ K+Tا ل اFاري إ;C *Oر از
Journal of Environmental Studies [JES] 2012. 9: 21-28
:*11ت ا'رة ا1TG [ و/ "و،1 اb/; ا ام "دةh,/) *1?/ * )ء دار1T1G *).G ،[Q;' "* ا،*1/0* اا ا." ."1ا .٢٠٠٥ ،٢ اد،١٣ ." اb,* ا-J ب زدة/* أ/ "درا، [/) ه */0* ا." ."رh ه );ق ا,هة اwف و.ا ،٤٣٧-٤٢٣ *FQ ،١٢ اد،٢٧ ." ،1 ;;?,وا .٢٠٠٩ 19, ا1VeG */ "درا،%/ 1- و هى1- @م/ ! C ا اا%F اء ا;ري ،1 ;;?,* وا/0* ا." ."*1 )0? اX +hا .٢٠٠٩ ,٦٠٥-٥٩٥ *FQ ١٦ اد،٢٧ ." ،"U1 وا;ر";آU11* ا+ *+' "ا،'F" 'ا :U1J,Ja?* اL ! [1Q, ا.٢٠١٠ http://www.perlite.com ." ااق1* ا);ق اQ" ،;ري. " اV *". ا،ءاتJl* اء وا/د);م ه .٢٠٠٠ ،*1 ;;?,ا _اضX. "ا،٢٨ %C* ر1C* اا1/1T* اQا';ا ،*1;ة ا1- وا11T, ز ا'آ ي0. ا."اء .١٩٨٨ *1 1;ص اF "ا،٢٧ %C* ر1C* اا1/1T* اQا';ا 11T, ز ا'آ ي0. ا." _اض اءX. .١٩٨٨ ،*1;ة ا1-وا Taneja, A. and Killo, F.,, "Development Of Hydrolic Binder Based On Gypsum Plaster”. Building Research Center, Baghdad, Vol. 6, No.2, ppp.50-63, (1987). Doxiad- QBE-5, 5, “Survey of the problems of Juss and Juss production in Iraq”. Building research Center, Baghdad, pp.1 pp.185, (1969). Khairia Al-Ramadani Ramadani and Taneja, G., "Development of Gypsum plaster products for use in buildings”. Building Research, search, R.P. 77/88, pp.37-40, pp.37 (1983). Mohan, R. Manjit, S. “Gypsum as a building material”, Central 32 Building Research, India, No. 14, pp. 1-6, (1983 1983). Malhorta H.L, ”Properties of materials at high temperature”. Journal of materials and structure, Vol. 15, pp. 170, (1982). ISO 3048-74, 74, “Gypsum PlastersPlasters General Test conditions” 1st edition, (1974). (
%١٥ *-) *11اري '\ت اF ا ل اXF :١٧ K+T
: درO ا اضoG"اh,/ ا% واهh "ا،%w آQ %/ ،*1 ;;?,"* ا. ا، د);مWF) ."*1 Jlا .٢٠٠٠ ،;ر-.* اق وا/ه ، ا;هب/ در وT ا,J\"* ا ا1d *1LT* اTF ا." وا;رة اءX.ام اh,/"إ .٢٠٠٢ ،٢ ص،*1C اا1',?ن وا/l;زارة ا ، ا;هب/ در وT ا,J\"* ا ا1d ."(X.* )ا واV_* و ا1 ا';اد اX +d" ت/ راT,د ا' وا/p !* ا_و1;اوة ا ،٢٤ ص،*1Cر* ااN* اC "&'* ا،*V_ا .٢٠٠٠ \ريFاري اء اF "ا ل ا،1` ا/ %أده *Q'ط اء ا; ا) وJ* أJرT"و ،*1) ا' اWF ا." دFG إ."1ا);ق ا .١٩٨٤ ،٢٩٧ -٢٩٢ ص،اد9) ;اصh ا1-FG" ,J'اF[ ا+1 ري واس. اFQ ."*\''ل ا';اد ا,/) اX. *1 1ا ،١ ء،٤." ،"h' ا' اGq';ث اF) ` Cو .١٩٨٩ ،١١٨-١٠٢ ص ;ر وا'دنh+ء ا1'1; آ1 " ،;T ا%?هة اJ ،١٠٢ ص." ااق.` اC ";ا-*1+ا .١٩٧٩ 1-FG" ،J'اF[ ا+1 ر ا و اس1 'F" . " اx,'ص اhع اT اX ;اصd ص،١ د،٧ ." ،;ث اءF) *." ،";يJHا .١٩٨٨ ،١٠٩-٨٥ , "ا- ا;هب ا/ وJ\"* ا ا1d ."ً آ';اد ز* ارX. وا1");ق اء ا ،(* ا';اد/ )هJH اJ* ا_رد1J'* ا/0' اGq" .١٩٩٩ ،٢٥٦-٢٤٥ ص،ا_ردن ;اصd m) 1-FG" ،;ي/;' ا%w! آ/;" [1T *اd تh" ف1* أOy) *1J/hا@ت ا * اء/ ه1,- " * أو."ا'دن .٢٠٠٠ ،*1 ;;?,"* ا. ا،ءاتJlوا
27
Journal of Environmental Studies [JES] 2012. 9: 21-28
Improve Thermal Insulation And Physical Properties Of The Iraqi Plaster Using Natural Additives Abstract Fires are considered to be one of the most common disasters in the buildings at the present time; therefore it becomes necessary to design the buildings with fire-resistant materials. Many types of stucco panels’ fire-resistant material have been created to prevent heat transfer to other parts of the institution, and to protect it from damage, so intensify increased to study how to improve the properties of the Iraqi plaster. Iraqi plaster differs from other types of plasters with its high quality mechanical and physical characteristics and this is because of the purity of its raw materials (rock stucco) and the advanced technology used in the production. However, there are some negative aspects that led to the lack of demand for it and, make it unsuitable for use as a binding agent, such as the lack of resistance to stresses tensile, lack of resistance to moisture and freezing speed leading to a significant loss of plaster during working with it, and thus lead to increased construction costs. In order to improve the properties of the Iraqi plaster many types of natural additives have been used in this research which are; Hay, Rice husks, sawdust and Alcaúlan, with a suitable ratios. The research also include studying the effect of this additives on physical and mechanical characteristic of Iraqi plaster, and studying the effect of the ratios of these additives on thermal insulation of the Iraqi plaster to choose the best additives type and to keep the high quality as possible of the material while maintaining the quality of the material and to make it remains within the standard specifications of plaster for construction purposes. Thermal insulation have been investigated after adding caúlan, Hay, Rice husks and sawdust with addition ratios of;3, 5, 10, 15% by weight of plasters. Results showed that the thermal insulation highly related to the ratio of water to plaster and with the type of the additives material. Increasing the ratio of natural additives led to an increase in the thermal insulation and this appears clearly with sawdust, Hay and Rice husks. While adding only small ratios of caúlan gives the highest thermal insulation bigger than other types of additives, this is because of its characteristic of losing the crystallization water, which constitutes approximately about 15% of its formulation when dealing thermally with it, but whenever caulan ratio increases the thermal insulation decreases due to the obstruction of the needle network formation.
28
Journal of Environmental Studies [JES] 2012. 9: 29-35
Original Paper
Germination of jojoba (Simmondsia chinensis L) seeds under the influence of several conditions Hassanein A. M.1, Galal E.2, Soltan D.1, Abed-Elsaboor K.2, Saad G. K.1, Gaboor G. M.1, El Mogy N. S.3 1
Central Laboratory of Genetic Engineering, Faculty of Science, Sohag University, 82524 Sohag, Egypt. 2 Genetics Department, faculty of Agriculture, Sohag University, Sohag, Egypt. 3 Al Obour Buildings 4, Salah Salem Road, Nasr City – Cairo, Egypt. Rec. 20 Mar, 2012 Accpt. 2 May, 2012
Abstract Our study indicates that jojoba is suitable plant for cultivation of the Egyptian marginal soils, in the desert area, where the seeds were germinated and grown in sandy soil of marginal fertility. To study the effect of NaCl and mannitol on seeds germination, jojoba seeds were placed on cotton layer flooded with solution containing different concentrations of them. Salinity stimulated seed germination, especially, when the seeds were subjected to relatively low concentration of NaCl (0.5 – 3 gm/l). Increase the concentration of NaCl over 3 gm/l resulted in inhibition of seed germination as well as radicle growth. Application of 2 or 3 gm/l mannitol in germination medium improved the seed germination, vice versa was detected under progressive increase of mannitol in germination medium. Mannitol as same as NaCl delayed seed germination of jojoba plant. On the other hand, jojoba seeds can be germinated in low frequency under high concentration of mannitol, up to 100 gm/l, when seeds were placed on three cotton layers just wetted by distilled water containing mannitol. Temperature may be the most critical factor during jojoba seed germination, therefore summer was the best season for seed germination; also, 30 oC was the best temperature degree for seed germination and emergence of radical in the shortest time. Key words: Desert cultivation, Jojoba, mannitol, sodium chloride, seed germination, stress. Plantations are established by using seeds, Introduction: Jojoba [Simmondsia chinensis (Link) seedlings, rooted cuttings, or plantlets Schneider] is a desert shrub which tolerates produced from tissue culture (Roussos et al., salinity and drought. The chromosome 1999; Roussos et al., 2006; Mohasseb et al., number of jojoba is 2n = 52 (Weiss, 1983). 2009). The male plants outnumber the Its natural life span appears to be between females when raised from seeds (Harsh et 100 and 200 years. Jojoba seeds contain a al., 1987). Jojoba plants obtained from seeds liquid wax of economic importance in showed a high variability in most industry (machine lubricant) as well as in characteristics including yield because it is medicine, where it can be used in cosmetics dioecious, and obligate cross-pollinated and anticancer compounds. Jojoba was used species (Gentry, 1958). Previous reports as a medicine for cancer, stomach ache, indicated that only a small proportion of the kidney disorders, easing childbirth and in plant population (less than 1%) originating tending wounds (Weiss, 1983). Jojoba has from seeds of native plants has the potential attracted interest as a landscape plant; also it to produce economically acceptable yields can be sued for soil conservation. The plant (Purcell and Purcell, 1988; Ramonet-Razon, has a deep root system; therefore it can be 1988). Therefore, comprehensive selection used in highway and roadside plantings and and breeding program was conducted in hedges. It can also be used as a soil stabilizer many countries all over the world to obtain in green belts around desert cities suffering elite cultivars. from particulate air pollution. It is the only Salinity is considered one of the most plant known that synthesizes liquid wax. The important factor restrict the horticultural seeds contain about 50% of simple wax production, especially in soils of the arid and esters of mono-unsaturated fatty acids and semi-arid regions on the earth. Few alcohols. economical plant species can be grown * Corresponding author: Dr. Hassanein A.M.
[email protected]
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Journal of Environmental Studies [JES] 2012. 9: 29-35
successfully in saline soil. It is worth to mention that the total area of arable land is gradually decreasing due to the progressive salinization of the soil (Botti et al., 1998). While jojoba is known as salt tolerant species (Jensen and Salisbury, 1988; Benzioni et al., 1992). salt damage can occur and differences in response among clones had been observed (Rasoolzadegan et al., 1980; Benzioni et al., 1992). indicating the possibility of developing clones with increased levels of salt resistance or tolerance. Elongation and thickening of stems (Bartolini et al., 1991). the total leaf area and leaf size (Bartolini et al., 1991). shoot and leaf expansion, number of leaves and flowers were reduced in response to increased levels of salinity (Rasoolzadegan et al., 1980; Benzioni et al., 1992). Increasing in leaf thickness was also reported when jojba plants were subjected to salt stress (Sa´nchez-Blanco et al., 1991). Benzioni et al., 1999 reported that some clones exhibited excellent vegetative traits related to yield potential such as a high survival rate, rapid growth, extensive branching, high node density, high flower density, high percentage of fruit set, high seed weight, and high wax content in the seed. The clones also differed in their wax composition. Under Egyptian condition, jojoba maximally utilizes 50-70 liters of water weekly in summer and 10-30 liters in winter but when it irrigated by flooding, 1215 irrigation times per year is needed. Mature shrubs characterize by their strong ability to survive without irrigation for long time where they can survive for a whole year without watering. Jojoba can also tolerate up to 3,000 p.p.m. without any impact to the yield. Therefore, Jojoba is considered one of the most practical and scientific solutions for desert plantation in Egypt. In spite of its importance, very few studies aim to understand the effects of abiotic stresses on the development and yield of the jojoba. This article covers the research on jojoba ecophysiology, with emphasis on the effects of water and salt stress on seed germination. Material and Methods: Plant material: For the experiments, seeds were obtained from the Egyptian Natural Oil Co. S.A.E., Ismailia Farm, Salam Zone, Manayef, Ismailia, Cairo, Egypt. The farm is
planted in Ismailia in 1991 and it is about 88,200sq.m of jojoba plants, it was used for research and production. Effect of soil type on seed germination: Thirty jojoba seeds were sown in plastic pots containing two Kg of soils composed from sand, soil or both according to the following table: Soil structure Sandy soil Clay soil 100% 0% 75% 25% 50% 50% 25% 75% 0% 100%
After 40 days percentage of seed germination and germination period were estimated. An emerged radicle was the criterion for germination (Côme, 1982). and the growth of the seedlings was laboratory or greenhouse conditions. Effect of season on seed germination: Thirty jojoba seeds were sown in plastic pots containing two kg of soil containing 1 and 1, sand and clay soil, respectively. After 40 days percentage of seed germination and germination period were estimated. Effect of temperature on seed germination: Jojoba seeds were grown on cotton in glass jars contained 50 ml Hogland solution and incubated at 30°C, 40°C, and room temperature (maximum 18°C). Germination frequency, length of roots, length of shoots and number of leaves per shoot were determined after four, nine, and 21 days of seedling. Effect of NaCl on seed germination: Under sterilized condition, Jojoba seeds were grown on cotton in glass jars contained 50 ml of Hogland solution supplemented with several concentrations of NaCl (0, 0.5, 1, 2, 3, 4 g/l). Jars were incubated at 30°C. Germination frequency, length of roots, length of shoots and number of leaves per shoot were determined after four, nine, and twenty one days of seedling. Effect of mannitol on seed germination: Jojoba seeds were flooded on cotton layer in sterilized glass jars contained 50 ml Hogland solution supplemented with several concentrations of mannitol (0, 0.5, 1, 2, 3, 4 g/l). Jars were incubated at 30°C. Germination frequency, length of roots, 30
Journal of Environmental Studies [JES] 2012. 9: 29-35
length of shoots and number of leaves per shoot were determined after four, nine, and twenty one days of seedling. In addition, jojoba seeds were placed on three cotton layers wetted with 50 ml and containing different concentration of mannitol. The percentage of seed germination was determined in 40 days. Results and discussion: The used jojoba seeds were usually smooth, brown to black in colour, their dimensions are 8 – 17 mm in length and 511 mm in cross-section. One hundred seed weight can vary from 61 - 157.8 gm/100 seed. Positive correlation was detected between seed size and oil content but the quality of the oil was exhibited very little variation regardless of the geographic origin of the seed (Yermanos, 1979). As was reported previously, the seeds contain little or no endosperm and consist mainly of the undifferentiated tissue of the cotyledons (Weiss, 1983). In this work, seeds were obtained after two months of harvesting date and they showed germination when they were subjected for suitable condition for seed germination. They were readily germinated in sandy or clay soil or in mixture from them under wide range of temperature from 18- 40 oC, it was in accordance with others studies (Gentry, 1958; Yermanos, 1982). Data in this work (Table 1) indicated that sandy soil is the most suitable soil for seed germination of jojoba plant, where it is expressed the highest percentage of germinated seeds in short time. Therefore, our study indicates that jojoba is suitable Age of seedling 3 days 5 days 7 days 15 days
plant for cultivation of the Egyptian marginal soils, in the desert area, where the plant can grow in sandy soil of marginal fertility and needs little water. It withstands salinity and it does not seem to need fertilizers or other polluting chemical treatments. Consequently, jojoba can be generally cultivated in well-drained, coarse, desert soils, where the soil is composed of sandy alluviums and mixtures of gravels and clays derived from such igneous materials as granitics and volcanics. For all of the previous reasons, jojoba is recommended for cultivation in Egyptian desert. Soil structure Sand Clay y soil soil
Percentage Germinat of seed ion germination period (%) (day) 100% 0% 75.0 13 75% 25% 65.0 15* 50% 50% 62.5 17* 25% 75% 55.0 21* 0% 100% 45.0 23* Table 1. Effect of soil type on percentage of seed germination and germination period.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution at 30°C at P < 0.05. Temperature may be the most critical factor in growing jojoba. Jojoba is living in the bright desert sun and tolerates the extreme daily fluctuations of temperature which commonly range through -1 oC during the morning to daily extremes of 46 oC (shade readings). In our work, increase of temperature stimulated seed germination, shortened the time needed for emergence of radical (Table 2).
Temperature of Seed germination Length of Shoot incubation freq. root freq. (℅) 30°C 61 0.26 --Room temperature 55* 0.2 --30°C 72 0.4 --Room temperature 55 0.53 --Room temperature 55 2 33 30°C 72 7 66 Table 2. Effect of temperatures on seed germination frequency.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution at 30°C at P < 0.05. Seed germination was influenced by temperature of the seasons. Seed germination in summer was higher than
Length of shoot --------1.5 0.8
winter (Table 3). Summer was the best season for seed germination it may be due to the highest temperature degree. Also, the shortest time of seed germination was detected when the seeds were subjected for the highest temperature in summer. Seedlings are more sensitive than mature 31
Journal of Environmental Studies [JES] 2012. 9: 29-35
tree (Weiss, 1983). While seeding is sensitive to light frosts of -1 or -2oC below freezing, mature shrubs are known to tolerate temperatures as low as -9 oC. When temperatures reach 50C flowers and terminal portions of young branches of most jojoba
plants are damaged. Wild jojoba plants can withstand very high temperature, cultivated cultivars showed maximum growth between 27 - 36 oC, but. Above 50 oC , the vegetative growth is suppressed, although not lethal (Weiss, 1983).
Parameter
Season Summer Autumn Winter Spring 77 ±3.81 63 ±2.00 58 ±3.81 73 ±2.50 Percentage of seed germination 13 ±1.00 17 ±1.00 26 ±2.00 17 ±1.52 Germination period / day Table 3. Effect of seasons on percentage of seed germination and germination period.
Under germination condition, the number of germinated jojoba seeds increased with time (Table 4, 5 and 6). In four days, salinity delayed seed germination of jojoba seed. While, 61% of seeds showed seed germination on NaCl free medium, 57% of seeds showed seed germination under the influence of 0.5 gm/l NaCl (Table 4). With time on germination medium, salinity stimulated seed germination (Table 5 and 6) especially, when the seeds were subjected for germination in the presence of relatively low concentration of NaCl (0.5 – 3 gm/l). In this work, the negative effect of NaCl on seed germination was detected when the seeds were subjected for 4 gm/l NaCl. While jojoba is known as salt tolerant species (Jensen and Salisbury, 1988; Benzioni et al., 1992), salt damage can occur and differences in response among clones had been observed (Rasoolzadegan et al., 1980; Benzioni et al., 1992). indicating the possibility of developing clones with increased levels of salt resistance or tolerance. Relatively low concentration of NaCl (0.53 gm/l) stimulated seedling growth and resulted in the formation of higher fresh mass than control. On the other hand, germination of seeds on medium containing 4 gm/l NaCl retarded seedling growth with complete avoidance of shoots (Table 5 and 6). Elongation and thickening of stems (Bartolini et al., 1991). the total leaf area and
leaf size (Bartolini et al., 1991). shoot and leaf expansion, number of leaves and flowers were reduced in response to increased levels of salinity (Rasoolzadegan et al., 1980; Benzioni et al., 1992). Increasing in leaf thickness was also reported when jojba plants were subjected to salt stress (Sa´nchez-Blanco et al., 1991). Conc. of Germination DRS NaCl (g/l) freq. (℅) Control 61 0.27 0.5 56.6* 0.17 1 38* 0.13 2 55.4* 0.6 3 44* 0.1 4 34.3* 0.1 Table 4. Effect of NaCl on seed germination after four days under germination condition.
* Means significantly different (t-test) from jojoba seeds cultured on hogland solution without salt at P < 0.05. Increase the concentration of NaCl over 3 gm/l resulted in inhibition of seed germination as well as radicle growth (Table 5). Plumules were completely suppressed when 4 gm/l NaCl were used. These results were in agreement with previous report (Berrichi et al., 2010). They were found that 5g/l of NaCl inhibited completely the emergence of plumules and, 3 g/l of NaCl marked the start of negative effect on the growth jojoba seedlings.
Conc. of Germination Length of root Shoot freq. Length of shoot NaCl (g/l) freq. (℅) (cm) (℅) (cm) Control 66 1.7 16 0.5 0.5 61* 5.3 16 0.3 1 66* 3 16 0.4 2 83 11 33* 0.4 3 75 7.25 33* 0.5 4 41* 0.23* ----Table 5. Effect of NaCl on seed germination after nine days under germination condition.
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Journal of Environmental Studies [JES] 2012. 9: 29-35
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without salt at P < 0.05. Relatively low concentration of NaCl resulted in enhancement of seedling growth up to 3 gm/l NaCl (Table 6). The data also indicated that 4 gm/l of NaCl resulted in decreasing the radical length and inhibition of plumule formation. Botti et al., (1998) reported that jojoba plants grown under high Conc. of NaCl (g/l)
Germination freq. (℅)
salt levels did not show much difference from those grown under non-saline conditions for most of the morphological and anatomical parameters such as number and size of stomata, density of trichomes, leaf size, branching characteristics and stem diameter. On the other side they found that leaf and cuticle thickness showed a high tendency to increase under saline conditions.
Length of root (cm)
Plumule Length of No. of No. of formation shoot (cm) leaves per shoots freq. (℅) shoot per seed Control 69 2 33.3 0.8 2 1 0.5 66.6* 6.66 50 1 2 1 1 66.6* 3* 50 1 3 1 2 83* 15.3 42.2 4 6 1 3 83.3 14.3 33* 2.3 4 1 4 50* 0.73* --------Table 6. Effect of NaCl on seed germination after fifteen days under germination condition.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without salt at P < 0.05. Mannitol as same as NaCl delayed seed germination of jojoba plant (Table 7). Application of 2 or 3 gm/l mannitol in germination medium improved the seed germination. Comparison between the effect of NaCl and mannitol indicated that incorporation of these both factors in relatively low concentration improved seed germination. Conc. of Germination Length of mannitol (g/l) freq. (℅) roots (cm) Control 61 0.27 0.5 46* 0.1* 1 55* 1.8 2 46* 0.46* 3 33* 0.16* 4 27* 0.1* Table 7. Effect of mannitol on seed germination after four days under germination condition.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without mannitol at P < 0.05. The data in this work indicated that the emergence of plumules were commenced after four days of subjecting the seeds for germination conditions (Table 8 and 9). The commencement of plumules was depend on the concentration of mannitol in the germination medium. While relatively low concentrations of mannitol (1 – 3 gm/l) stimulate plumule formation, 4 gm/l mannitol inhibit completely the emergence of seed plumule. The same results were obtained when 4 gm/l NaCl were used (Table 6).
Conc. of Germination Length of Plumule Length of mannitol freq. (℅) roots (cm) freq. (℅) shoots (cm) (g/l) Control 66 1.7 16 0.5 0.5 55.5* 1.15* 16 0.5 1 55* 8.5 50 0.3 2 66* 7 33 0.2 3 83 3.3 25 1 4 50* 0.5* ----Table 8. Effect of mannitol on seed germination after nine days under germination condition.
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Journal of Environmental Studies [JES] 2012. 9: 29-35
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without mannitol at P < 0.05. Plumule formation were delayed under the influence of 4 gm/l mannitol where it was only commenced in two weeks (Table 9). On
the other hand, in two weeks, 4 gm/l mannitol stimulated the radical length in comparison to that of control. These data indicated that mannitol in concentration between 1 and 3 m/l stimulated both shoot length and the number of shoots per seed.
Conc. of Germination Length of Plumule Length of No. of No. of mannitol freq. (℅) roots (cm) freq. (℅) shoots (cm) leaves per shoots (g/l) shoot per seed Control 66 2 33 0.8 2 1 0.5 55.5* 2 33 0.8 2 1 1 58* 14.6 50 3.16 2 2 2 83 9 33 1.1 2 1 3 83 7.66 83 1.81.8 2 3 4 50* 5.7 30* 0.66 --1 Table 9. Effect of mannitol on seed germination of seeds placed on one layer of cotton flooded with Hogland solution for fifteen days.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without mannitol at P < 0.05. Placing jojoba seeds on three cotton layers just wetted by germination medium created suitable condition for seed germination although the presence of high concentration of mannitol. Under these conditions, jojoba seeds were able to germinate and form plumule up to 100 gm/ mannitol. Comparision between data in tables 9 and 10 indicated that seed germination was strongly Treatment 0 86
10 96
20 86
30 80
affected by the presence of high water content in germination medium. It was expected since the plant strongly tolerates drought condition but it is sensitive for frost and water flooding. Consequently, jojoba has recently established as a crop in many arid and semi-arid regions of the world (Brown et al., 1996), especially around the Mediterranean basin (Benzioni and Dunstone, 1986; Mills et al., 1997) because it is drought and salt tolerant plant species.
Mannitol concentration (gm/l) 40 50 60 70 80 76* 63* 60* 56* 46*
90 43*
100 36*
110 20*
Percentage of seeds cultured (%) 8 7 9 11 11 13 15 16 17 19 21 25 Germination period (day) 18 27* 12* 10* 8* 7* 6* 5* 3* 2* 1* 0 N .of shoot formation Table 10. Effect of mannitol on seed germination of seeds placed on three layers of cotton and witted with distilled water solution for fifteen days.
* Means significantly different (t-test) from jojoba seeds cultured on distilled water without mannitol at P < 0.05. The data of his work indicated that jojoba is the most suitable plant for the Egyptian conditions especially in desert area. Under Egyptian condition, jojoba maximally utilizes 50-70 liters of water weekly in summer and 10-30 liters in winter but when it irrigated by flooding, 12-15 irrigation times per year is needed. Mature shrubs characterize by their strong ability to survive without irrigation for long time where they can survive for a whole year without
watering. Jojoba can also tolerate up to 3,000 p.p.m. without any impact to the yield. Therefore, Jojoba is considered one of the most practical and scientific solutions for desert plantation in Egypt. References: Bartolini, G., Mazuelos, C., Troncoso, A., (1991). Influence of Na2SO4 and NaCl salts on survival, growth and mineral composition of young olive plants in inert sand culture. Adv. Hortic. Sci. 5, 73–76. Benzioni, A., Nerd, A., Rosengartner, Y., Mills, D. (1992). Effect of NaCl salinity on growth and development of jojoba clones I.
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Journal of Environmental Studies [JES] 2012. 9: 29-35
Young plants. J. Plant Physiol. 139, 731– 736. Benzioni, A, Shiloh, E., Ventura, M. (1999). Yield parameters in young jojoba plants and their relation to actual yield in later years Industrial Crops and Products 10: 85–95. Berrichi, A., Tazi, R., Bellirou, A., Kouddane, N., Bouali A. (2010). Role of salt stress on seed germination and growth of jojoba plant Simmondsia chinensis (Link) Schneider. IUFS J Biol 69:33-39 Botti, C., Palzkill, D., Munoz, D., Prat, L. (1998). a. Morphological and anatomical characterization of six jojoba clones at saline and non-saline sites. Ind. Crops Prod. 9, 53–62. Brown, J.H., Palzkill, D., Whittaker, C., (1996). The jojoba industry 1994, a status and update. In: Princen, L.H., Rossi, C. (Eds.), Proc. of the Ninth International Conf. on Jojoba and Its Uses, and of the Third International Conf. on New Industrial Crops and Products, 25–30 September 1994, Catamarca, Argentina, pp. 150–154. Côme, D. (1982). Germination. In: Mazliak P., ed. Croissance et développement. Physiologie végétale. II. Paris: Hermann, 129–225. El Mogy, N.S. (1999). Egyptian Experience in Planting Jojoba Fourth International Water Technology Conference IWTC 99, Alexandria, Egypt 431. Jensen, W.A., Salisbury, F.B. (1988). Bota´nica, 2nd ed. Libros McGraw-Hill de Me´xico, Me´xico, 722 pp. Harsh, L.H., Tewari, J.C., Patwal, D.S. and Meena, G.L. (1987). Package of Practices for Cultivation of Jojoba (Simmondsia chinensis) in AridZone, Pp: 1–19. CAZRI, Jodhpur (India). Mohasseb, A.H., Mohamed, K., El-Bahr, M.K., Adam, Z.M., Moursy, H.A. and Solliman,
M. (2009). In Vitro Clonal Propagation of Jojoba (Simmondsia Chinensis (Link) Schn.). Aus tralian Journal of Bas ic and Applied Sciences , 3: 3128-3136. Rasoolzadegan, Y., Hogan, L., Palzkill, D.A. (1980). Response of jojoba to five levels of salinity. In: Puebla, M. (Ed.), Proc. of the IV International Conf. on Jojoba, 5–6 November 1980, Hermosillo, Sonora, Mexico, pp. 113– 120. Roussos, P.A., Tolia-Marioli, A., Pontikis, C.A. and Kotsias, D. (1999). Rapid multiplication of Jojoba seedlings by in vitro culture. Plant Cell, Tissue and Organ Culture 57: 133–137. Roussos, P.A., Tsantili, E., Pontikis, C.A. (2006). Responses of jojoba explants to different salinity levels during the proliferation stage in vitro Industrial Crops and Products 23: 65–72. Sa´nchez-Blanco, M.J., Boları´n, M.C., Alarco´n, J.J., Torrecillas, A. (1991). Salinity effects on water relations in Lycopersicon esculentum and its wild salt-tolerant relative species L. pennelli. Physiol. Plant. 83, 269– 274. Weiss, E.A. (1983). Crambe, niger and jojoba. In: Oilseed Crops. Longman, London, UK, pp.507 - 527. Yermanos, D.M. 1979. Jojoba - a crop whose time has come. California Agriculture (Jul Aug.), pp. 4 - 11. Yermanos, D.M. (1982). Jojoba - A potentially valuable species in the control of desertification. Proceedings of the Conference on Alternative Strategies for Desert Development and Management, 31 May - 10 June 1977, United Nations Institute for Training and Research, Sacramento, California, USA. Agriculture Vol. 2, pp. 374 - 381.
ا ا
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35
Journal of Environmental Studies [JES] 2012. 201 9: 37- 42
Original Paper
$ر "! اة ا ذي ان ا وان ا إزا اات وا')('ت !& او%ت ا*! و 7-= %0 -ا) .ر 8 ،١Yف 8Rن )V0 ،٢-.8د ,V%0ه:اع -;0 ،٣أن ،٤
٥
١
أذ 2V< / 8V0ه ا / 7* )0R / c-.ا)اق 0رس 2V< / 8V0ه ا / 7* )0R / c-.ا)اق ٣,٤,٥ 0س 2V< /ه ا / 7* )0R / c-.ا)اق
٢
إ3م ١٩ :أ( .< ،٢٠١٢ل٢٠١٢ 0 ٢٨ :
ا:567 * 2ه6ا ا M%.اjر; 0'; ,-ا$%ة ا" ذي ان ا Vوان ا إزا اات وا ت 5-0 ,0او+ت ا (-1"* 2* M-+ ،-:و ,-./0 ,-*+وا+ة *)( 'م ا$%ة ا" ذات ا ا و8د أب ان ا Vوا$ ()* -;kب ان 8و*34 5- 61* 7ت 9$0 -:0ذة ,0 إ+ى %0ت ا ) 7* 0أن 2إ0اره .4< .= >8ن :% (D."0) -;)0ااد ا -و )0 ,0د9ل ا+ة 2* M-+ا" (-1ر+ Rارة ا 7- ../ا lIأن ا8د أب ان .0 8ع )- :0ج ون * * ق 2-< n 9ااد ا .Pا6ا .Iا TDS -وا --ا -Iوا ,+آ * ,-.إن أ (4إزا ات و CODا وا6اب 8د أب ان 71 M-+ 71 M-+ 8آ ءة اNزا %٦٣.٥و ٩١.٨٥ات واـ >8 CODاا و 7P+أ (4إزا ت ا6اب 8د أب ان .V0 8ق :ج و ءة إزا ،%٩٦ 71أ 0أ$% -.-* QIP9 (4ة * 2اP%ل 8 -8ا8د أب ان 8وأب ان .0 8ع :ج 2-< U$* 2 .اTس ا -رو 5-0 -Rاو+ت $ب ان. ا ت ا8ا :إزا اات ،إزا ا ت'; ،م ا$%ة ا" ،او+ت ا ،-:ان ا ،Vان ا. ا:8$ *)ف 5-0ا 34ت ;$أي 5-0أو ا%* (Iي = >8ا ZIأو U0ت "( ،Zا ،(Iأو rزات أو 0آ *.اآ* :-ن ]رة إذا P c-. 7+sرة ر) -V-Iد وRد ا"ا 5-0 ZIا 34ت إ> وRد ااد ا .Pاء وااد ا .Pر *ن 48 أو )-.s 48 -rور * t8 (" Rو rوي وذا ZIأو =$ل %0 /0ةKaria& ) . .(Christian, 2006 ,0أز ااد ا +s 2إ> ا%Vت ا-I ه اات و ا ت وأن زد* ا%Vت ا-I u 8 lهة اUNاء ا61ا >8 ZR D6 IاV;Nن إزا أو ا-U$* ,0 (-jه ) Marthie and Cloete .(1998 ) ;'م ا$%ة ا" ذات ا ا ,0 ا ';Tا -%ا ) إزا اات وا ت :-ه ل ز ,0اث ا -رو%* M-+،-ج -8ا Rإ> اTوآ (% ,-Vاو ,-Rإ> ;ات * -ن ا) -ا ) Nزا اات ه -8 w8ا Rوا *-1 2ب اTوآ ,-Vوا /z0 ٠.٣آ 7-اـ lIإن إزاـ اـ Vر * ,V%آ ا; n /ز ,0اـث اـ -رو n /* - -اـ .Vاـ V cر اـ$%ة :دة 8اـ$%ة. أRى اk+.ن ) (Sotirakou et al., 1999درا >8 -j+إ+ى ا%ت ا)$ 0ب ا$%ة ا" ذات ا ا وا *)0 5-0 lو+ت j0 |Pار ١٢٠٠٠ 5م/٣م و*39 ,-.ل ارا أن ه 56ا (:* %ا (" -;0Tآ 5-0 ,0 (0او+ت و* ,0 %٢٨ (:اـ Vر اـ)4ي و ,0 %١٥اـ Vر اـ وآ; .V; 7اـ Vر اـ:اـ/اـ ZاـI-- xوآ ,-Vاـ:اـ ه r/z0 ٨ام. 8اTرض lI; 7- M-+ارا أن إزا او* ,-Rاو,- 7+ )* 08 % (٥٤ – ٣٢ن اTرض :0 -rرو8 =Tر -زادت ; .VاNزا (Pإ> )(٨٧ – ٤٧ * 08 %ن اTرض ا 0/Vا) :0رو8 =Tر.و إزاـ اـ ت *او% (٥٤ – ٣٢) ,- 7+ * 08ن اـ$رض :0 -rرو 8ـ=$ر -زادت ; .Vاـزاـ (Pإ> )* 08 % (٨٧ – ٤٧ن اTرض اـ 0/Vاـ)ـ :0رو 8ـ=$ر. ا)اد وAا@? ا>:. * 2ه 56ارا *" (-1و ,-./0 ,-*+وا+ة *)( 'م ا$%ة ا" ذات ا ا و8د 38
أب ان ا Vوا$ ()* -;kب ان 8و*34 5- 61* 7ت 9$0 -:0ذة ,0 إ+ى %0ت ا ) 7* 0أن 2إ0اره .4< .= >8ن :% (D."0) -;)0ااد ا- و ,0 )0د9ل ا+ة 2* M-+ا" (-1ر+ Rارة ا ./و]^ ا"( ر8 -V0 9ى 5-0ا 34ت Y-ا sاف 4ن = U %آ U$ا |Pق ا" 7.U M-+ %ان اا tj% M-% (9ز0 ,0ث ه-روj0 -ار.8 ٢٤ 5 Inlet Outlet Sed. Aeration Tank tank 28 cm 8 cm Diffuser
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)%ض ان ":4 =( )+ (k (٢ض ان -8 2* M-+ 8 ا) ا ,-]+أا; -ا"( ,0اD3. ا" ف (2٢٦) jوار* ع ) (2٢٥و 61* 2آ( وا +ـ ١٠آ( دورة () M-+اTول (8 * ,0: )j0 (Reactار 8 ٢٤ 5وا8 ٢٤ (8 * ,0: ;k Yj.Vا +اTو> :0 -8ج jة ,-8 و) Y.jا +ا:0 -8 -;kج ة .,-8 26 cm
^] (٢) ./أ)د +ض ان 8ا/Vم * 6-ارا.
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*39 2ل ة ارا إRاء ا %ت ا-و ا)-j jس ) (CODواس ا -روpH -R و,ECو TDSوSalinityو PO4و NO3و*آ :-ا8 8 اـن اـ.V ,-+ا; 74 /آ ءة اـزاـ إ> 8 %٧٧.٨٨ وRد :0 -8ج ة -8 (.< ,-8اـ +ض اـن ـ 8و):ى Z.ذ Dإ> أن -8اـ:ج *V )V0ات اـ-+$ء اـ >j. 0 2V< ()R 0 8ـ jو*8 ,0 :ر 5اـ 5-اـ)ـ 0زاد ,0 *آ :-اـ CODاـ (Technical Learning ).College, 2003
90 80 70 60 50 40 30 20 10 0
0
* 8ا+Tاض 0ا;)* >8 wآ :-ا آ ءة أ8 -Iها3 ا-Ij;اض ا+Tا ة ان" رVة ا" ا$%ا ( ) ا0R ، ا- آ,-VR0 ات+ام و/ "ا.(١٩٩٩) 7-= %0 - و،Y ر.)ا )0 0T اs ة ا" ذات ا$%ا ، ا- آ،-VR0 +وs أ،"ت+ او5-0 .( ) ا0R ;ن8 ، د و+ %0 ،د+ ى و،ر+ - ا5- ا,0 "إزا اات.(٢٠٠٩) صj0 R-.( ا8 )ل ا -آ,- )م ا7* 0 ،",-VوآTا ٣ ا)د،١٦ ا،7* )0R ، ا 41
Journal of Environmental Studies [JES] 2012. 9: 37- 42
Vaboliene, G., Matuzevicius, A.B. and Dauknys, R. (2007). "Impact of temperature on biological phosphorus removal from wastewater in Lithuania" EKOLOGIJA. 2007. Vol. 53. No. 4. 95–101 WPCF, APHA and AWWA (1999) "Standard Methods for the Examination of Water and Wastewater " 20th ed, Washington D.C. USA Zou, H., Du, G.C., Ruan, W.Q. and Chen, J. (2006). "Role of nitrate in biological phosphorus removal in a sequencing batch reactor". World Journal of Microbiology & Biotechnology, 22: 701–706.
Technology Conference, IWTC9 2005, Sharm El-Sheikh, Egypt. Sotirakou, E., Kladitis, G., Diamantis, N. and Grigoropoulou, H. (1999). "Ammonia and Phosphoures removal in municipal waste water treatment plant with extended aeration" Global Nest:the Int J ,Vol.1,No.1 , 47-53. Su, J.L. and Ouyang, C.F. (1996). Nutrient removal using acombined process with activated sludge and fixed biofilm. Wat.Sci. Tech, Vol.34, No.1-2, 477-486. USEnvironmental Protection Agency (2003). (ACTIVATED SLUDGE)State Acceptance List USA, Office of water, Washington.
Comparison Between Continuous and Batch Flow Activated Sludge Reactor to Remove Nitrate and Phosphate From Domestic Wastewater Waleed M. Sh. Alabdraba, Afaf J. Obed, Masuod M. Hazaa, Safa Badeaa and Manolea Aiden
Abstract In this paper a comparison between continuous and batch flow activated sludge reactor to remove nitrate and phosphate from domestic wastewater, tow bench scale units was operated one work as continuous reactor and the second as batch reactor, the raw wastewater brought up from one of the lifting pump stations in Tikrit city and pass it throw metal screen to prevent floating materials from entering the units. The results shows the batch flow reactor followed by mixing without aeration is the best in bring down total dissolved solids , electrical conductivity and salinity while the best removal of nitrate 63.5% and chemical oxygen demand 91.85% achieved in batch flow reactor. The best removal of phosphate is 96% achieved in batch flow reactor with mixing only before the aeration. the batch flow reactor and the batch flow reactor followed by mixing give the best settling characteristic of sludge, while the pH don’t affected by the flow regime. Key Words:-Nitrate Removal, Phosphate Removal, Batch Flow, Continuous Flow
42
Journal of Environmental Studies [JES] 2012. 9: 43- 51
Original Paper
Modeling of the heating transfer in the karst aquifers for Val d'Orléans city (France) Ali Salim Joodi Department of Environmental Eng., Collage of Engineering, Al-Mustansiriya Univ, Baghdad (Iraq) Rec. 17 Nov, 2011 Accpt. 12 Dec, 2011
Abstract: In karst aquifers, temperature distribution play an additional important role since they carry information about internal aquifer structures. The aim of the present work is to develop a two dimensional heat transfer model in a karst aquifer. Navier Stokes equation is used to simulate the groundwater velocity in the conduit system where the porosity tends to one, and means water velocity was taken into account in the fractured rock. Heat transport equation was applied to simulate the temperature distribution in a karst aquifer, and k- turbulent model is used to simulate the turbulent viscosity. The model was applied to the karst system of Val d'Orléans. Temperatures are measured in thirteen wells with different depth in 29 Jun 2011. Results have shown that the model was not sensitive to the variation of water density, but it is sensitive to the variation of specific heat and density of the rock especially in the fractured system. Also, the model was varied sharply with the velocity of water in sinkhole points, and any variation in the depth of saturated zone. The comparison between measured and calculated temperatures in wells is very good. Key word: Karst aquifers, Heat transport, Conduit and diffuse flow systems, Numerical model and Val d'Orléans highly vulnerable compared to other Introduction: Karst forms when groundwater dissolves groundwater systems, since potential pockets of limestone, dolomite, or gypsum in contaminants can easily reach the groundwater bedrock. This dissolution process increases the (Genthon et al., 2005; O’Driscoll and bulk permeability of the massif, developing a DeWalle, 2006; Dogwiler et al., 2007). conduit network of high hydraulic The use of heat as a groundwater tracer, in conductivity, with short water residence time, contrast to the use of chemical tracers, is and preserving micro fractured blocks with attractive because of the ease of measuring long water-residence time (Dogwiler et al., temperature with high precision (errors as low 2007). Thus, karstification provokes flow as ±0.03 _C). Groundwater temperatures are heterogeneity, increasing the permeability influenced by the temperature of recharge, contrast between conduit flow and diffuse mixing of different waters resulting from flow systems. Karst system is mainly groundwater flow. (Andrieux, 1978; Crowther characterized by four elements. The first is and Pitty, 1982; Roy and Benderitter, 1986; sinkholes which recharge the karst system. Lastennet, 1994; Martin and Dean, 1999; Birk The second is the underground drainages or et al., 2004). have used water temperature conduits which are largely influenced by jointly with other natural hydro dynamical and sinkholes and consequently the water flow in hydro chemical responses, as additional these regions is high. The third is fractured information to characterize the different flow system (diffused system) which is weakly types and the structural influenced by sinkhole and consequently the organization of drainage patterns in karst water flow in these regions is slow. The last is aquifers. Groundwater applications have been spring point in which the water is emerged at developed to model quick-flow in karst the surface. In this context, karst systems are conduits, diffuse flow in fractured and, and the * Corresponding author: Dr. Ali Salim Joodi
[email protected]
43
Journal of Environmental Studies [JES] 2012. 9: 43- 51
interaction of these two flow regimes. Fluid flow and solute/ heat-transfer numerical models that include both of these flow regimes include (Benderitter et al., 1993; Liedl and Sauter, 2000; Birk, 2000; Andre and Rajaram, 2005; Birk et al., 2004). With these distributed-parameter models, velocities are estimated from the flow simulation and then are used in the transport simulation. Additional insight into general heat-transfer theory for pipe and channel flow is described by (Gnielinski, 1976; Aravinth, 2000; Beek et al., 1999; Benim et al., 2004). As the conduits are highly influenced by the contamination of rivers (as the water of sinkholes), any information on conduit locations usually is unavailable. For cases where wells or springs have a temperature response that is influenced by conduit flow, the conduit network is globally defined. This paper presents a twodimensional numerical water flow /heat transport model that is explored as an alternative that might be useful to locate the conduit networks in the karst system of the Val d'Orléans. This model simulates the temperature response to recharge in wells and assumes that wells receive at least some of its water from a nearby conduit. The water flow will be simulated in conduit system by Navier Stokes equation, but the model does not simulate the water flow in the fractured system (in which the permeability is less than that in the conduit system). The water velocity in the fractured system will be carried out as mean velocity. The results of the model will be verified with temperatures observed in the wells. The viscosity gradient will be calculated by using K epsilon turbulent model. Characteristics of the experimental field area: The karst aquifer of the Val d’Orléans is the largest in France in terms of flow rate (10 m3/s) and provides the mean water resource of the Orléans city (Albéric and Lepiller, 1998). The Val d’Orléans is considered as a vast depression of the major bed of the Loire river, 37 km long and from 4 to 7 km wide (Fig. 1). The karst aquifer is hosted within an Oligocene carbonate lacustrine deposit occurring in the center of the Paris basin and
called the limestone of Beauce (Guillocheau et al., 2000). This latter formation display variable repartition with a significant primary porosity except for micritic facies, this porosity is increased by karstification leading to a relative high permeability (5E-10 to 2E-9 m2) at hectometric scale (Martin and Noyer, 2003). The latter is overlapped by the quaternary alluvia of the Loire river. The Loire river feeds more than 85% of the water hosted in the carbonated karstic aquifer. The estimated inflow of the Loire river in the sinkhole infiltration area of Jargeau varies from 15 to 20 m3/s and it can reach 100 m3/s during floods (Zunino, 1979; Chéry, 1983; Lepiller and Mondain, 1986). Karst networks are well known in the left bank of the Loire river. The water runs from Jargeau through the karst conduits networks towards the direction of the springs of the Loiret river, (Zunino, 1979; Chéry, 1983; Lepiller and Mondain, 1986), as shown in figure (1). The springs of Loiret river are called the Bouillon and the Abîme, they are considered as the main emergences of the water lost close to Jargeau in the Loire river (from 0.3 to 5 m3/s). The mean aquifer outflow is an underground emergence in the Loire river located around the confluence of Loire - Loiret. Previous studies showed the relation between these springs and the sinkholes points at Jargeau within the Loire river using dye tracer tests (Zunino, 1979; Chéry, 1983; Albéric and Lepiller, 1998; Lepiller, 2001; Albéric, 2008). The main karstic conduits were located according to the depressions of the piezometric surface and to the different connections identified by the tracer tests presented in figure (1).
Figure (1): Underground waters karstic circulations of the Val d’Orléans city (Albéric and Lepiller, 1998).
44
Journal of Environmental Studies [JES] 2012. 9: 43- 51
Governing equations: Numerical simulations of fluid flow and heat transport in a karst aquifer were used to investigate the temperature distribution in the karst and by consequence to determine the karstification degree of the karst aquifer. In the present work, Navier Stokes equation is applied to simulate the water velocity in conduit system, as a result to the grand porosity in this system. A uniform velocity is taken in the fractured rock system where the porosity is highly less than that in conduit system. To determine the temperature distribution in the karst, heat transport equation is used. Due o the variation of the temperature in the karst system, the viscosity will be changed, and to calculate this variation K epsilon turbulent model is used. Navier Stokes equation for two dimension is: w
q w q w w q w p 2q w w g t
(1) Heat transport equation in the karst for two dimension is: (1 )r Cr T w Cw T q ww CwT 2T t (2)
K epsilon turbulent model for two dimension is: w
w
k q w w k 2 k G w E t k
(3)
q w w 2 t
(4)
2 C1 G C2 w k k
To calculate the turbulent viscosity, the following equation is used: t C w
k2
…………(5)
Where:
w
is the water density, qw is water velocity vector, t is the time, p is the water pressure, g
is the acceleration gravity, is the porosity of the karst system, r is the rock density, C r is the specific heat of the rock, C w is the specific heat of the water, T is the water temperature, is the heat conductivity, k is the turbulence kinetic energy, is the dissipation rate of
turbulent kinetic energy, G is the production
of turbulence kinetic energy, k , , C1 , C 2 , C
are constants. Les valeurs des constantes sont (Leschziner et Rodi, 1983).
C 0.09 , C1=1.44, C2=1.92, =1.3, k =1 In the present work, the variation in the density of water and rock can be calculated from equations (6) and (7), respectively. The variation in the specific heat of water and rock can be calculated from equation (8) and (9), respectively (Somerton, 1992; Douglas and Jacob, 2004). w (T ) 1043.196 - 42.966623exp (0.006895T) (6) r (T )
2650 1 (T 20) 0.5 10 4
1 C w (T ) 0.0002374 8.06817 108 T 8.03671 1010 T 2
Cr (T ) 1234.257 - 454.546exp (-0.0039733T)
(7) ..(8) (9)
Heat transport in the karst system of the Val d'Orléans: Karst system of the Val d'Orléans has many sinkhole points which are located on the Loire river at the city of Jargeau, and it has many spring points as shown in figure (1). In this work, the temperature is monitored at thirteen wells and one spring point located in the karst system of the Val d'Orléans. In general, water in the conduit includes sinking river water and diffuse flow (from fractured system) entering the conduit along its length. In addition to water from the conduit, a well or spring also might receive local diffuse flow that has not interacted with the conduit. For example, a well that is south of the conduit may induce flow from the conduit and also from diffuse flow within the well’s zone of influence on the north, south, and east sides of the well (Fig. 2) and consequently it can be observed a variation in the water temperature of the well. But in the most cases, it can be observed many wells in which the temperature is constant. This can be attributed to the location of the well, the variation of the water temperature in the well decrease when the well far away from the conduit and vice ve
45
Journal of Environmental Studies [JES] 2012. 9: 43- 51
21000 m Sinkhole point Spring source Fractured system
4000 m
Conduit system Well
Figure (2): Schematic diagram of a karst system
Figure (4): Water temperatures measurements in wells of Ligne, Piezometre, Moret 2, and Moret Well of Boires 1 Well of Boires 1
Well of Ligerienne Well of Ligerienne 21
23
20
22 21 20
18
Temperature (C)
Temperature (C)
19
17 16 15 14 13 12 13
18
S
14 13 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28
Depth (m) Well of 2 2 Well ofBoires Boires
Well of Ormeaux 21
22
20
21
19
19
18
Temperature (C)
20 18 17 16 15 14 13 12 7
8
9
10
11
12
13
14
15
16
17
18
19
17 16 15 14 13 12 8
20
10
12
14
Depth (m)
16
18
20
22
24
26
28
Depth (m)
Figure (5): Water temperatures measurements in wells of Ligerienne, Boires 1, Ormeaux, and Boires 2. Well of of Berruet 1 Well Berruet 1
Berruet 3 WellWell of ofBerruet 3 22 20
Le Berruet 4
Temperature (C)
Temperature (C)
16 14
Le Berruet 3 Le Berruet 1 Le Berruet 6
Well location
8
10
12
14
16
18
20
22
24
26
28
17 16 15 14 13 8 10 12 14 16 18 20 22 24 26 28 30 32 34 36 38 40 42 44
30
Depth (m)
Well of 4 Well ofBerruet Berruet 4
Well of Berruet 6
Well of Berruet 6
22
22
21
21
20
20
19 18 17 16 15 14
19 18 17 16 15 14 13 12
12 7
9
11
13
15
17
Depth (m)
19
21
23
25
6
27
8
10
12
14
16
18
20
22
24
Depth (m)
Figure (3): Wells location in the karst system of the Val d'Orléans
Berruet 7 7 WellWell ofofBerruet
o
22 21
Temperature (C)
In these wells, the variation reaches to 12 C, this means that these wells are close to the conduit system. But the temperature is stable in wells of Ligerienne and Ormeaux. Figure (6) shows the wells of Berruet 1 and Berruet 3 are affected by the conduit system but less than that in wells of Boires 1 and Boires 2.
18
Depth (m)
13
Le Berruet 7
19
12
6
Temperature (C)
Le Moret
18
12
Temperature (C)
la Piézométrie
Width (m)
Les Boires 2 Les Ormeaux Les Boires 1 La Ligérienne
La Ligne
E
15
21
Le Moret 2
W
16
Well of Ormeaux
20
Bouillon spring
17
23
22
Loire river
N
18
Depth (m)
Length (m)
Loiret river
19
12 8
Temperature (C)
Depending on the previous description, the temperature is monitored at thirteen wells and one spring point located in the karst system of the Val d'Orléans. Position of wells in the calculational region is illustrated in Fig. (3). The temperature measurements in wells are shown in figures (4,5 and 6). These measurements are provided in 29/06/2011 when the temperature of Loire river and the Bouillon spring were 26.5 oC and 15.6 oC, respectively. figure (4) shows that the water temperature in wells of Ligne, Piezometre, and Moret is nearly stable but in the well of Moret 2, the temperature deceases 3 oC starting from the depth of 12 m. This variation in the temperature can be attributed to the water coming from the conduit system. The variation of groundwater temperature in wells of Boires 1 and Boires 2 is greater than that in the well of Moret 2, as shown in figure (5).
20 19 18 17 16 15 14 13 12 7
9
11
13
15
17
19
21
23
Depth (m)
Figure (6): Water temperatures measurements in wells of Berruet 1, Berruet 3, Berruet 4, Berruet 6, and Berruet 7
46
Journal of Environmental Studies [JES] 2012. 9: 43- 51
and 9). The initial values of water viscosity, kinetic energy and dissipation rate of turbulent kinetic energy are obtained by the following equations: … (10) 0.077U* h … (11) Sgq w
21000 m
470 m
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1
Sinkhole points
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.8
Bouillon spring
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.10.10.10.10.10.10.10.10.10.80.10.80.80.1
Sinkhole points
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.10.10.10.10.10.10.10.10.10.80.10.80.10.10.1
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.80.10.10.10.10.10.10.80.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.80.10.10.10.80.10.10.10.80.80.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.80.10.10.10.10.10.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.10.10.10.10.10.10.10.10.80.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.10.10.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1
4000 m
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.10.10.10.10.10.10.80.80.80.80.80.80.10.10.10.1
Where: h is the mean water depth (depth of saturated zone in the karst aquifer), S is the piezometric of the water slope, U* is the friction velocity which is equal to ghS . The piezometric of the water slope is calculated in each region in the study area according to the piezometric map provided by (Zunino, 1979). Equation (5) is used to calculate the initial value of turbulent kinetic energy. Boundary conditions of the study area are illustrated in fig (8). The finite differences technique is used to solve partial differential equations in the present numerical model. The length and width increments are 5 m. Also, the final time of the model is three months and the time step is 5 min, and the thermal conductivity is 1.3 J/sec.m. oC. u ,v,T ,K ,E 0 y
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1
Figure (7): Porosity field and conduit system pathway suggested in the karst system of the Val d'Orléans (Lepiller, 2001; Albéric, 2008).
Loiret river
u, v, T, K, E 0 x W
P
P
h2
N
Initial conditions constitute values of velocity, temperatures, density and specific heat of the water and rock, water viscosity, turbulent kinetic energy and dissipation rate of turbulent kinetic energy. Concerning the velocity, it is carried out the velocity value measured during the summer season. Then the water velocity inlet to the conduit system is 75 m/hr, this velocity is varied in the conduit system according to Navier Stokes equation, but it is constant in the fractured rock matrix. The velocity inlet to the fractured rock system is a half of previous velocity. Initially the temperature in the study area is that measured in the Bouillon spring on 29 Jun 2011, it was 15.6 oC, expect on the sinkhole points on the Loire river in which the initial water temperature is that measured on Loire river, it was 26.5 oC on 292011. The initial values for the density and specific heat of the water and rock are calculated from equations (6, 7, 8,
Loire river
E
h1 h2 s L
L
S
h1
P: Sinkhole points on Loire river S: Water slope h: Water level
P
Initial values
Mathematical modeling: The study area in the karst aquifer of the Val d'Orléans starts from Jargeau (where the sinkholes on the Loire river are existed) to the last spring point on the Loiret river. The study area is considered as a rectangular area with the length 21000 m and the width 4000m. Two dimension numerical model is carried out to simulate the water temperature distribution in the karst system of the Val d'Orléans. The porosity in conduit system and in the fracture rock system is 90% and 10% respectively. The pathway of the conduit system suggested in the present research is shown in figure (7). This pathway is suggested according to (Lepiller, 2001; Albéric, 2008).
u ,v,T ,K ,E 0 y
Figure (8): Boundary conditions of the two dimension numerical model
Results and discussions: Many parameters influence on the water temperature distribution in a karst aquifer, as the depth of saturated zone, water velocity, viscosity and density effects, porosity, density and specific heat of the rock. Therefore, it was important to study the effect of the variations of these parameters separately to describe the rate and pattern of heat transport and prioritize their influences. Neglecting the density difference between the temperature of Loire river and groundwater temperature is carried out to study the effect of density on the temperature distribution, and keeping a constant density 47
Journal of Environmental Studies [JES] 2012. 9: 43- 51
during a time period of study equal to initial groundwater density. A comparison between isotherms with and without density effect is shown in fig (9). It can be clearly observed, all isotherms are not influenced by the change of water density. This due to the small temperature difference between Loire river temperature (26.5 oC) and groundwater temperature (15.6 oC). To investigate the effect of the variation of water slope along the study reach which is coming from the piezometric map, a constant water slope along the study reach is taken into account. From fig (10), it can be observed that the water slope parameter influences on the behavior of temperature distribution. When the water slope is varied, the distribution of temperature levels advances more in transverse direction as that when the water slope is constant. Length (m)
a
18000
20000
16000
14000
12000
10000
8000
6000
4000
2000
0
500 1000
2000 2500 3000
°C Width (m)
1500
3500 4000
Length (m)
b
18000
20000
16000
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12000
10000
8000
6000
4000
2000
0
500 1000
Width (m)
1500 2000 2500 3000 3500 4000
a) When the water density is varied as a function of temperature b) When the water density is constant along the study reach
Figure (9): Effect of water density on the behavior of groundwater temperature distribution.
The water velocity in sinkhole points on Loire river has a great effect on the behavior of temperature distribution along the study reach. As shown in fig (11), all isotherms are advanced longitudinally and transversely with any increase in the water velocity values. This phenomenon can be attributed to the effect of advective term in the heat transport equation, which is responsible for the advance of isotherm along the study reach. Fig (12) shows the effect of water depth in the saturated zone. According to Albéric and Lepiller (1998). the mean depth of saturated zone for the karst system of the Val d'Orléans is 25 m. Any decrease in the depth of saturated zone causes a retardation of the temperature isotherms along the study reach, as shown in fig (12). This can be attributed to the effect of the depth of saturated zone on the friction velocity and water viscosity and by consequence on the temperature distribution. In order to show the effect of the variation of the specific heat and the density of the rock on the behavior of the temperature distribution, equations (7) and (9) are neglected. This means that the specific heat and the density of the rock are constant in the calculations. In the case of the specific heat and the density of the rock are constant, all isotherms are retarded in the transverse direction, but they are advanced in the longitudinal direction, as shown in fig (13). This may be due to the effect of the specific heat and the density of the rock on the domain of fractured system in the karst aquifers only.
Length (m)
a
20000
18000
16000
14000
12000
10000
Length (m) 8000
6000
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2000
a
0
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Length (m) 20000
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Length (m) 20000
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1500
Width (m)
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3500 4000
a) When the water slope is varied along the study reach b) When the water slope is constant along the study reach
Figure (10): Effect of water slope on the behavior of groundwater temperature distribution.
a) When the water velocity is 75 m/hr b) When the water velocity is 144 m/hr
Figure (11): Effect of water velocity on the behavior of groundwater temperature distribution.
48
Journal of Environmental Studies [JES] 2012. 9: 43- 51
Length (m)
a
20000
18000
16000
14000
12000
10000
8000
6000
4000
2000
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1500 2000 2500 3000 3500 4000
Length (m)
b
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0
500 500 1000 1000
Width (m)
1500 1500 2000 2000 2500 2500 3000 3000 3500 3500 4000 4000
a) When the depth of saturated zone is 25 m b) When the depth of saturated zone is 5 m
Figure (12): Effect of the depth of saturated zone on the behavior of groundwater temperature distribution. Length (m)
a
20000
18000
16000
14000
12000
10000
8000
6000
4000
2000
0
500 1000
2000 2500 3000
°C Width (m)
1500
3500 4000
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b
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Measured Calculated % temperatur temperatur Erro e e r 15.1 15.7 3.9 Berruet 1 16.2 16 1.2 Berruet 3 13.3 15.1 13.5 Berruet 4 17.3 16 7.5 Berruet 6 17.6 17.8 1.1 Moret 22.1 20.1 9 Boires 1 14.4 15.1 4.8 Ligne 12.9 15.2 17.8 Piezometri 17.3 17.1 1.1 Moret 2 eBoires 2 18.8 18.5 1.5 20.5 20.5 0 Ligerienne Bouillon 15.6 15.1 3.2 spring (1): Comparison between measured and Table calculated temperatures in wells. Well
2000
0
500 1000
2000 2500
Width (m)
1500
3000 3500 4000
a) When the density and specific heat of the rock is varied b) When the density and specific heat of the rock is constant (density= 2649.13 kg/m3, specific heat= 825.1 J/kg.k)
Figure (13): Effect of the density and specific heat of the rock on the behavior of groundwater temperature distribution
In order to verify the accuracy of the present numerical model, a comparison between measured and calculated temperatures in wells is occurred. The best results are obtained when the water velocity in sinkhole points is 80 m/hr, the porosity is 10% in the fractured system and 80% in the conduit system and the depth of saturated zone is 25 m. Table (1) displays this comparison with the percentage error for each well. It can be clearly observed that the results of the model are very good compared with the measured temperature. The percentage error of the model ranges from zero to 17.8 percent.
Conclusions In karst aquifers, temperature signals play an additional important role since they carry information about internal aquifer structures. A two dimension heat transport numerical model was developed to simulate the temperature distribution in a karst aquifers composed conduits and fractured systems. The model was based on the Navier Stokes equation to simulate the groundwater velocity in the conduit system where the porosity tends to one, heat transport equation to simulate the temperature distribution in a karst aquifer, and finally k- turbulent model to simulate the turbulent viscosity. The model was applied to the karst system of the Val d'Orléans. This system is very developed in which there are many sinkhole points on the Loire river and many spring point along the Loiret river. Temperatures are measured in thirteen wells with different depth in 29 Jun2011 when the temperature of Loire river and the Bouillon spring were 26.5 oC and 15.6 oC. Calculated results have shown that the model is not sensitive to the variation of water density, but it is sensitive to the variation of specific heat and density of the rock especially in the fractured system. Also, the model is very sensitive to any variation on the water velocity in sinkhole points, and any variation in the depth of saturated zone. The influence of the variation of the groundwater slope along the study reach is small compared 49
Journal of Environmental Studies [JES] 2012. 9: 43- 51
with other parameters. The best results are occured when the water velocity in sinkhole points is 80 m/hr, the porosity is 10% in the fractured system and 80% in the conduit system and the depth of saturated zone is 25 m. Finally, it was observed that the comparison between measured and calculated temperatures in wells is very good. References Albéric, P. and Lepiller, M. (1998). Oxydation de la matière organique dans un système hydrologique karstique alimenté les pertes fluviales (Loiret, France). Water Resources 32, 2051– 2064 Albéric, P. (2008). Les trios pertesémergences (ou inversacs) du domaine de la source (Loiret). Colloque national d’Hydrogéologie. May 16 and 17, Orléans –France Andre, B.J., Rajaram, H. (2005). Dissolution of limestone fractures by cooling waters: Early development of hypogene karst systems. Water Resources Research 41 (1), 1–16. Andrieux, C. (1978). The experiences form the temperature in the karst (in French). Colloque de Tarbes, Le karst: son originalité physique, son importance économique. Association des Géologues du SudOuest (AGSO), Orleans, France, 48–63 Aravinth, S. (2000). Prediction of heat and mass transfer for full developed turbulent fluid flow through tubes. International Journal of Heat and Mass Transfer 43, 1399–1408. Beek, W.J., Muttzall, M.K., van Heuven, J.W. (1999). Transport Phenomena, second edition. John Wiley & Sons Ltd., West Sussex, England. 329 p. Benderitter, Y., Roy, B., Tabbagh, A. (1993). Flow characterization through heat transfer evidence in a carbonate fractured medium: first approach. Water Resources Research 29 (11), 3741–3747. Benim, A.C., Cagan, M., Gunes, D. (2004). Computation analysis of transient heat transfer in turbulent pipe flow.
International Journal of Thermal Sciences 43, 725–732. Birk, S. (2002). Characterization of Karst Systems by Simulating Aquifer Genesis and Spring Responses: Model Development and Application to Gypsum Karst. Tübinger Geowissenschaftliche Arbeiten, vol. 60. Reihe C. Institut und Museum für Geologie und Paläontologie der Universität Tübingen, Tübingen, Germany. . Birk, S., Liedl, R., Sauter, M. )2004(. Identification of localized recharge and conduit flow by combined analysis of hydraulic and physico– chemical spring responses (Urenbrunnen, SW-Germany). Journal of Hydrology 286: 179–193 Chery, J.L. (1983). Etude hydro chimique d’un aquifère karstique alimenté par perte de cours d’eau (la Loire). Thèse 3e cycle, Orléans Crowther, J., Pitty, A.F. (1982). Water temperature variability as an indicator of shallow-depth groundwater behaviour in limestone areas in west Malaysia. Ournal of Hydrology 57, 137–146 Dogwiler, T., Wicks, C.M., Jenzen, E. (2007). An assessment of the applicability of the heat pulse method toward the determination of infiltration rates in karst losing stream reaches. Journal of Cave and Karst Studies 69 (2), 237– 242. Genthon, P., Bataille, A., Fromant, A., D’Hulst, D., Bourges, F. (2005). Temperature as a marker for karstic waters hydrodynamics. Inferences from 1 year recording at la Peyrere cave (Ariege, France). Journal of Hydrology 311 (1–4), 157–171. Gnielinski, V. (1976). New equations for heat and mass transfer in turbulent pipe and channel flow. International Chemical Engineering 16 (2), 359– 368.
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Guillocheau, F., Robin, C., Allemand, P., Bourquin, S., Brault, N., Dromart, G., Friedenberg, R., Garcia, J., Gaulier, J., Gaumet, F., Grosdoy, B., Hanot, F., Le Strat, P., Mettraux, M., Nalpas, T., Prijac, C., Rigollet, C., Serrano, O., Grandjean, G. (2000). Meso-Cenozoic geodynamic evolution of the Paris Basin: 3D stratigraphic constraints Geodin. Acta 133(4), 189– 246 Lastennet, R. (1994). Role of unsaturated zone in the functioning of karst aquifers: approach for the physico–chemical and isotopic study of input and output (springs) of Ventoux massif (Vaucluse) (in French). PhD Thesis, Univ. Avignon and Pays de Vaucluse, France, 239 pp Lepiller, M. (2001). Traçages appliqués à la dynamique des aquifères karstiques. Géologue (129), 79–84 Lepiller, M. and Mondain, P.H. (1986). Les traçages artificiels en hydrogéologie karstique. Hydrogéol 1, 33–52 Liedl, R., Sauter, M. (2000). Characterization of karst groundwater processes, using models of aquifer genesis and heat transport. Grundwasser 5 (1), 9–16. Martin, J.B., Dean, R.W. (1999). Temperature as a natural tracer of short residence
times for groundwater in karst aquifers. In: Palmer AN, Palmer MV, Sasowsky ID (eds) Karst Modeling. Spec. Publ. 5, Karst Waters Institute, Leesburg, VA, 236–242 Martin, J.C. and Noyer, M.L. (2003). Caractérisation du risque d’inondation par remontée de nappe sur le Val d’Orléans. Etude hydrogéologie, BRGM O’Driscoll, M.A., DeWalle, D.R (2006). Stream–air temperature relations to classify stream–ground water interactions in a karst setting, central Pennsylvania, USA. Journal of Hydrology 329 (1–2), 140–153. Roy, B., Benderitter, Y. (1986). Natural thermal transfer in a superficial fissured carbonate system (in French). Bull Soc Géol France 2 (4), 661–666 Yakhot, V., Orszag, S.A., Thangam, S., Gatski, T.B. and Speziale, G.C. (1992). Developments of Turbulence Models for Shear Flows by a Double Expansion Technique, Physics of Fluids A, 4 (7), 1510–1520 Zunino, (1979). Contribution à l’étude hydrogéologique du Val d’Orléans. Ph.D. thesis, Orleans University
الملخص العزبى
)نمذجت نقل الحزارة في طبقت المياه الجوفيت الكارستيت لمدينت اورليانز (فزنسا :الخالصت ْذف ْزا انؼًم. دسخخ انحشاسح رهؼت دٔس يٓى خصٕصب نًؼشفخ يؼهٕيبد حٕل رشكيت ْزِ األٔسبط،في األٔسبط انكبسسزيخ اسزخذيذ نحسبة انسشع فيNavier Stokes يؼبدنخ.ْٕ رطٕيش ًَٕرج سيبضي ثُبئي األثؼبد االَزشبس انحشاسح في انكبسسذ . ٔرى اخز قيًخ يؼيُخ ٔسطيخ نهسشػخ في انٕسط انًزشقق،)conduit( انٕسط انكبسسزي انزي ركٌٕ فيّ انُفبريخ رًيم نقيًخ ٔاحذ نحسبة انزغيش في قيىk- ٔرى اسزخذاو يٕديم،يؼبدنخ اَزقبل انحشاسح اسزخذيذ إليدبد رٕصيغ دسخبد انحشاسح في انكبسسذ حيث رى قيبط دسخبد انحشاسح،) انًُٕرج انشيبضي رى رطجيقخ في انُظبو انكبسسزي في يذيُخ ٔسنيٌٕ (فشَسب.انهضٔخخ انذايًُيكيخ انُزبئح ثيُذ أٌ انًُٕرج ال يزأثش ثأي رغيش في انكثبفخ ٔنكُّ حسبط ألي رغيش في.29 Jun 2011 في ثالثيٍ ثئش يبئي ثزبسيخ كزنك أٌ انًُٕرج حسبط خذا ألي رغيش في قيًخ انسشع انذاخهخ نهُظبو.كثبفخ انصخٕس انكبسسزيخ خصٕصب في انٕسط انًزشقق إٌ انًقبسَخ ثيٍ قيى دسخبد انحشاسح انًقبسخ ٔانًحسٕثخ ثيُذ أٌ انًُٕرج.انكبسسزي ٔ أي رغيش في قيًخ ػًق انًُطقخ انًشجؼخ .خيذ خذا
51
Journal of Environmental Studies [JES] 2012. 9: 53-63
Original Paper
Characteristics of the Hydraulic Jump in Trapezoidal Channel Section Sadiq Salman Muhsun Environmental Engineering Dept., College of Eng. Al-Mustansiriya University, Baghdad, Iraq. Rec. 17 Nov, 2011 Accpt. 12 Dec, 2011
Abstract In this study, characteristics of the hydraulic jump in trapezoidal channel sections were analyzed and a general equation represents the solution of the hydraulic jump in the channels of arbitrary cross-sections (rectangular, triangular & trapezoidal) was driven depending on the momentum principle. The solution of the models was provided using Newton Raphson method. Consequently, Tables and charts of family curves of the conjugate depths ratio (r=y2/y1) have been prepared, for a very wide range values of Froude numbers and section ratios (k=b/zy). For each type of cross sections, the efficiency of the energy dissipation of the hydraulic jump was also analyzed and compared with each others. The relationship between the initial and sequent Froude numbers (FD1 and FD2) has been indicated for various values of k1=b/zy1. Depending on the results of conjugate depths ratio r = y2 / y1, the length of the hydraulic jump were estimated for a very wide range of k1=b/zy1, using two suggested models. It was found that the channel shape has insignificant effect on the efficiency of the energy dissipation of the hydraulic jump, although the triangular section tends to be more efficient than the others by about 10 percent in higher FD1. When (FD1 > 6), the velocity head after the jump could be neglected. When the section ratio k1 is approximately 3, the length ratio of the hydraulic jump (Lj / y2) reaches to a maximum value independent on the value of FD1. In all cases, it was shown that the comparison of the theoretical results with other experimental data indicate a very good agreement Key words: hydraulic jump - sequent depth ratio - jump in trapezoidal and triangular channels - Conjugate Depth, Energy Dissipaters Introduction The hydraulic jump is a natural phenomenon which may be defined as a sudden and turbulent passage of water from supercritical flow to subcritical state, (Modi, 2004). The abrupt change in flow condition is accompanied by considerable turbulence and energy losses. The hydraulic jump commonly occurs with natural flow conditions and with proper design can be an effective means of dissipating energy at hydraulic structures. Expressions for computing the before and after jump depth ratio (conjugate depths) and the length of jump are needed to design energy dissipaters that induce a hydraulic jump. For this reason, the hydraulic jump is often employed to dissipate energy and control erosion at storm water management structures.
Hydraulic jumps are commonly experienced in rivers, canals, industrial applications and manufacturing processes. (Montes, 1979; Chow, 1994; Treske, 1994; Reinaur and Hager, 1995; Chanson and Montes, 1995; Chanson, 2007 and Murzyn, 2007; studied the undular hydraulic jump, described its characteristics where the values of the Froude number in which the jump is no longer undular was calculated neglecting the effect of the channel width. The jump height, however, may be predicted quite accurately using momentum theory alone Hotchkiss et al., (2003). Typically, the discharge and upstream depth are already known, and what remains to be determined is the downstream “sequent depth”, Chadwick et al., (2004). The purpose of this study, is to develop a general solution of the sequent depth problem in trapezoidal channel section * Corresponding author: Dr. Sadiq Salman
[email protected]
53
Journal of Environmental Studies [JES] 2012. 9: 53-63
(rectangular, triangular & trapezoidal), based on the momentum principle law. Such a solution will be useful to analyze the characteristics flow of a turbulent hydraulic jump and to determine the length of the hydraulic jump as well as the efficiency dissipation. Momentum Principle Because of energy losses, the size and location of the hydraulic jump cannot be predicted using the energy equation. However, because momentum is conserved across hydraulic jumps under the assumptions of this study, momentum theory
could be applied to determine the jump size and location Hotchkiss et al., (2003). Figure 1 indicates the control volume used and the forces involved. Distribution of pressure in the upstream and downstream sections is assumed to be hydrostatic. So, applying the momentum equation in a frictionless channel considering the above assumptions, leads the momentum equation in the term of the specific force to be: Q2 Q2 + Z C 1 A1 = + Z C 2 A2 = F gA 1 gA 2
F1 = F
Or
(1) (2)
2
2
V1 /2g
jump
E2
E1
2
V2 /2g y2
y1
Fig.1: Hydraulic jump control volume .
Where: F: Specific force Q: Flow rate g: Gravity acceleration A1 & A2: Cross-sectional area before and after the jump, respectively. ZC1 & ZC2: Distances of the centroids sections from the free surface area before and after the jump, respectively. Consider that:
A = by + zy
T = b + 2 zy F
r
=
V gy
F
D
=
V gD
2
(3) (4) (5) (6)
Where: T: Top width of the sectional area. b: Bottom width of the sectional area. z: side slope V: Mean velocity. Fr: Froude number in term of the depth of flow y. FD: Froude number in term of the hydraulic depth D = A/T.
Now, define a dimensionless factor k to be a section ratio such that:
k=
b
(7)
z y
Consequently, Eqs. (3 & 4) could be rewritten as: (8) A = zy 2 ( k + 1)
T = zy(k + 2)
(9)
Also, it could be seen that: k+2 Fr k +1
FD =
(10)
According to the section ratio k, the shape of the channel section will take the following form: when k = 0, the section is a triangular shape. and, when k = ∞, the section is a rectangular shape. While for 0 < k < ∞, the section is a trapezoidal shape. By taking the moments about the top axis of a trapezoidal channel section, the centroid Position Zc, could be determined as:
Z
C
=
1 1 k + 2 3 k + 1
y
(11)
54
Journal of Environmental Studies [JES] 2012. 9: 53-63
Substituting the values of various terms of Eq. 2, considering Eqs. (7 to 11) and simplifying, the specific force before the jump F1 will take the following form: 1 4 2 F (k + 3 k + 2 ) + k + k + (12) 2
F1 = Z y 1
2
2
r
3
2 (k + 2 )
3 1
3
By the same way, it could be seen that: Fr 3 F2 = Z y 2
2
(k
2
1 + 3k + 2 + k 2 (k + 2 )
)
2
4 2 + k + 3 3 2
(13)
Where the subscripts 1 & 2, refer to the corresponding variable of section 1 and 2 respectively. It is necessary now to represent the variables of Eq.13 in term of the same variables of the section 1, considering that:
k2 =
b = r −1 k 1 zy 2
(14)
Where: r: Conjugate depths ratio of the initial and sequent depths, (y2 / y1) . Also, it could be seen that: A1
2
A2
2
Fr
= r
2
= r
2
or F r
2
2
k1 + 1 k1 + r
−2
−1
A1
2
A2
2
(15)
2
Fr
k +1 = r − 3 1 k1 + r
2
(16 a)
1
2
Fr
2
(16 b)
1
So, Eq.13 will take the following form: −2 r Fr 3 F2 = Z y 2
2
k +1 k+r
2
(r
−2
k
2
1 + 3 r −1 k + 2 + r −1 k 2 (k + 2 r )
Satisfy the condition of Eq.2, taking in the count Eqs. (10, 12, & 17), the following
)
2
+
4 2 k + r 3 3 1
equation is produced after some tedious mathematical steps:
3 2 5k 3 3k 2 (k +1) 2 (k +1) 2 k (k +1) r −3FD r + +1 r + +1 (k +1) r + +k −3FD =0 2 (k +2) (k +2) 2 2 4
Equation 18 represents the relationship of the Conjugate depths ratio of a hydraulic jump in a horizontal trapezoidal channel. This equation could be simplified by considering that: 5k B = + 1 2
(19 a)
3k C = + 1 (k + 1) 2
(20 a)
k2 2 ( k + 1) (k + 1) D = + k − 3FD 2 (k + 2)
E = −3FD
2
( k + 1) 3 (k + 2)
(21 a)
(22 a)
Where k is k1 and FD is FD1. So, Eq. 18 will reduce to the following form:
r4 + B r3 +C r2 + D r + E = 0
(23 a)
(17)
(18)
Conjugate Depths - Initial and Sequent Depths: For a given values of FD1 and k1, the solution of Eqs. (18 or 23a) represents the conjugate depths ratio r = y2/y1. As it is known, this Equation has four roots. The signs of the second and the third term of Eq.23a (B & C) are always positive, while the fifth term E, is always negative. The forth term D, may have a positive or a negative sign depending on the values of FD1 and k1. According to Decard theory, equation 23 has always a unique positive root whatever the sign of the term D, and that is the required solution, (Hoffman, 2001). The researcher found that Newton–Raphson method is a very good technique to provide the results. Also, fixed-point method may be a useful alternative technique to determine the mathematical solution for the depths upstream and downstream of the hydraulic jump, (Vatankhah, 2008). Fig.2 represents a dimensionless chart for the conjugate depths 55
Journal of Environmental Studies [JES] 2012. 201 9: 53-63
yi 2 = 0 . 5 1 + 8 F rj yj
− 1
(
A = B = 1 + 2. 5 k 2 + 1. 5 k 2
2
2
)
C = 1 + k 2 − 3k 2η 2 − 3k 2 η 2
(
2
D = − 3η
E = − 3η
k=0 k=0.5 k=1 k=2 k=3 k=4 k=6 k=8 k=10 k=15 k=20 k=30 k=40 k=60 k=100 Rect.
25
20
15
10
5
0 0
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
FD 1=V/(gD)0.5
Fig.2: Family curves for the conjugate depths ratio r, corresponding to the upstream Froude number FD1 and k1.
(24)
In many practical and designed cases the problem is to find the initial depth y1 for a given control depth y2 in the downstream of the jump. In this case the following model (Eq.23 b), will be used to provide the conjugate ratio r,, which depends on the relationship between Eqs. (10 , 14 & 16) and Eq.18. The solution of this model was achieved by trail and error method with helpful of the computer. However, all the results were represented in Fig.3 and Table 2.
(
30
r = y2/y1
ratio r for various upstream Froude numbers FD1, corresponding to a very wide range of a section ratio k1, from zero (i.e., triangular shape) to infinity (i.e., rectangular shape). As it is shown, the conjugate depths ratio has a little significant change at high section ratios for the same Froude numbers. ers. Also, for all values of k1, when FD1 < 2, the conjugate depths ratio r is near the corresponding value of the rectangular section. In case of the rectangular section (where k1 = ∞), the curve indicates a completed agreement with the results of the standard ndard form of the hydraulic jump usually used in a rectangular channel section, Eq.24. For more details, notice Table 1.
− 6 k 2η
2
(19 b)
)
(20 b)
)
(21 b)
2
Fig.3: Family curves for the conjugate depths ratio r, corresponding to the Downstream Froude number FD2 and k2.
It could be seen that, when FD2 is more than 0.5 the conjugate depth ratio (r =y2/y 1) has the same value for any section ratio k2 . For this reason the arrangement values of FD2 in Table (2) was concentrated on the low values of FD2. Fig (4) shows the relationship between the upstream Froude number FD1 and the corresponding FD2 for varies values of k1. The Figure indicates that when FD1 is greater than 20, the minimum value of FD2 approaches to 0.1 for the triangular section and 0.15 for the rectangular section. Indicating that the shape of the section has a little effect on the values of FD2 when FD1 is greater than 2 and has insignificant effect when the value of FD1 is less than 2.
(22 b)
1.0 0.9 k1=0
2
k +1 k +1 η = Fr = 2 r5 2 FD22 rk2 +1 k2 + 2
0.8
2 1
(22 C)
k1=5 k1=10
0.7
k1=100 0.6 FD2
2
Rect. k=∞
0.5 0.4 0.3
Therefore,
Eq.
18
will
be:
0.2 0.1
4
3
2
A r + B r +C r + D r + E = 0
0.0
(23 b)
0
2
4
6
8
10
12
14
16
18
20
FD1
Fig.4: Relationship between FD1 and FD2 for varies values of k1.
56
Journal of Environmental Studies [JES] 2012. 9: 53-63
F
k1=0
k1=.5
k1=1
k1=2
k1=3
k1=4
k1=5
k1=6
k1=7
k1=8
k1=9
k1=10
k1=12
k1=15
k1=20
k1=30
k1=40
k1=60
k1= 100
Rect. k=∞
Rect. Eq.24
1.000 1.702 2.284 2.799 3.271 3.710 4.125 4.519 4.897 5.261 5.952 6.606 7.228 7.825 8.399
1.000 1.842 2.545 3.170 3.741 4.275 4.778 5.257 5.716 6.157 6.998 7.792 8.549 9.274 9.972
1.000 1.935 2.726 3.432 4.079 4.684 5.255 5.800 6.321 6.823 7.780 8.683 9.545 10.370 11.165
1.000 2.051 2.963 3.785 4.543 5.254 5.927 6.569 7.186 7.780 8.912 9.983 11.004 11.984 12.928
1.000 2.120 3.112 4.015 4.853 5.641 6.389 7.104 7.791 8.454 9.719 10.917 12.061 13.158 14.216
1.000 2.165 3.215 4.179 5.078 5.926 6.732 7.505 8.248 8.966 10.338 11.639 12.882 14.076 15.227
1.000 2.197 3.290 4.301 5.249 6.145 7.000 7.820 8.610 9.374 10.835 12.222 13.549 14.824 16.054
1.000 2.220 3.348 4.397 5.384 6.321 7.216 8.076 8.905 9.708 11.246 12.708 14.106 15.452 16.750
1.000 2.238 3.393 4.473 5.494 6.464 7.394 8.288 9.152 9.989 11.593 13.120 14.583 15.990 17.350
1.000 2.253 3.430 4.536 5.585 6.585 7.544 8.468 9.362 10.229 11.892 13.477 14.997 16.460 17.874
1.000 2.264 3.460 4.589 5.662 6.687 7.673 8.623 9.543 10.437 12.153 13.790 15.361 16.874 18.338
1.000 2.274 3.485 4.633 5.727 6.775 7.784 8.758 9.702 10.619 12.383 14.068 15.685 17.244 18.752
1.000 2.289 3.525 4.705 5.834 6.920 7.968 8.982 9.967 10.925 12.772 14.539 16.238 17.878 19.466
1.000 2.304 3.568 4.783 5.952 7.081 8.175 9.237 10.271 11.279 13.227 15.095 16.895 18.636 20.325
1.000 2.320 3.614 4.868 6.084 7.264 8.413 9.533 10.627 11.696 13.770 15.768 17.699 19.571 21.391
1.000 2.337 3.663 4.962 6.231 7.473 8.689 9.881 11.051 12.199 14.439 16.610 18.719 20.772 22.775
1.000 2.346 3.689 5.012 6.312 7.589 8.845 10.081 11.297 12.495 14.839 17.122 19.347 21.522 23.649
1.000 2.354 3.716 5.065 6.398 7.715 9.016 10.301 11.572 12.828 15.299 17.718 20.091 22.419 24.705
1.000 2.362 3.738 5.109 6.471 7.823 9.165 10.496 11.817 13.128 15.721 18.276 20.797 23.283 25.738
1.000 2.372 3.772 5.179 6.589 8.000 9.412 10.825 12.238 13.651 16.478 19.305 22.133 24.961 27.789
1.000 2.372 3.772 5.179 6.589 8.000 9.412 10.825 12.238 13.651 16.478 19.305 22.133 24.961 27.789
D1
1 2 3 4 5 6 7 8 9 10 12 14 16 18 20
Table. 1. Conjugate depths ratio of a hydraulic jump in trapezoidal channel sections for a given y1 with varies k1.
F D2
k2 = 0
k2 = 0.05
k2 = 0.075
k2 = 0.1
k2 = 0.15
k2 = 0.2
k2 = 0.25
k2 = 0.3
k2 = 0.35
k2 = 0.4
k2 = 0.45
k2 = 0.5
k2 = 0.55
k2 = 0.6
0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0.55 0.6 0.7 0.8 0.9 1
8.219 5.518 4.176 3.375 2.843 2.466 2.183 1.964 1.789 1.646 1.527 1.340 1.199 1.089 1.000
9.786 6.158 4.511 3.575 2.974 2.555 2.247 2.011 1.824 1.672 1.547 1.351 1.205 1.091 1.000
10.619 6.486 4.679 3.675 3.038 2.599 2.278 2.033 1.841 1.685 1.556 1.356 1.207 1.092 1.000
11.472 6.818 4.848 3.774 3.102 2.642 2.308 2.055 1.857 1.697 1.565 1.361 1.210 1.093 1.000
13.207 7.485 5.184 3.970 3.226 2.726 2.368 2.099 1.889 1.721 1.583 1.371 1.215 1.095 1.000
14.932 8.145 5.514 4.161 3.347 2.808 2.425 2.140 1.919 1.744 1.600 1.381 1.220 1.097 1.000
16.608 8.789 5.835 4.346 3.464 2.886 2.480 2.179 1.948 1.765 1.617 1.390 1.225 1.099 1.000
18.212 9.409 6.144 4.524 3.576 2.961 2.532 2.217 1.976 1.786 1.632 1.398 1.229 1.101 1.000
19.732 10.003 6.441 4.695 3.684 3.033 2.583 2.253 2.002 1.805 1.647 1.407 1.233 1.103 1.000
21.164 10.568 6.725 4.858 3.787 3.102 2.630 2.288 2.028 1.824 1.661 1.414 1.237 1.104 1.000
22.507 11.103 6.994 5.014 3.885 3.167 2.676 2.320 2.052 1.842 1.674 1.422 1.241 1.106 1.000
23.766 11.608 7.250 5.162 3.978 3.230 2.719 2.351 2.074 1.859 1.687 1.429 1.245 1.107 1.000
24.943 12.083 7.492 5.302 4.067 3.289 2.761 2.381 2.096 1.875 1.699 1.435 1.248 1.108 1.000
26.045 12.531 7.721 5.435 4.151 3.346 2.800 2.409 2.117 1.890 1.710 1.442 1.251 1.110 1.000
Table. 2. Conjugate depths ratio of a hydraulic jump in trapezoidal channel sections for a given y2 with varies k2.
57
Journal of Environmental Studies [JES] 2012. 9: 53-63
F D2
k2 = 0.7
k2 = 0.8
k2 = 0.9
k2 = 1
k2 = 1.25
k2 = 1.5
k2 = 1.75
k2 = 2
k2 = 2.5
k2 = 3
k2 = 3.5
k2 = 4
K2 = ∞ Rect.
Eq.24
0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0.55 0.6 0.7 0.8 0.9 1
28.041 13.350 8.142 5.681 4.307 3.450 2.873 2.462 2.155 1.919 1.731 1.453 1.257 1.112 1.000
29.793 14.074 8.518 5.902 4.447 3.545 2.939 2.509 2.190 1.945 1.751 1.464 1.263 1.114 1.000
31.336 14.718 8.854 6.100 4.574 3.630 2.999 2.552 2.222 1.968 1.768 1.474 1.268 1.116 1.000
32.702 15.290 9.154 6.278 4.688 3.707 3.053 2.591 2.250 1.989 1.784 1.483 1.273 1.118 1.000
35.499 16.472 9.778 6.651 4.929 3.870 3.168 2.675 2.312 2.035 1.818 1.502 1.282 1.122 1.000
37.637 17.382 10.264 6.943 5.118 4.000 3.260 2.741 2.361 2.072 1.846 1.517 1.290 1.125 1.000
39.311 18.098 10.648 7.176 5.270 4.104 3.334 2.795 2.401 2.102 1.869 1.530 1.297 1.128 1.000
40.649 18.673 10.958 7.364 5.394 4.190 3.395 2.840 2.434 2.127 1.888 1.540 1.303 1.130 1.000
42.638 19.532 11.423 7.649 5.581 4.319 3.488 2.909 2.485 2.166 1.917 1.557 1.311 1.134 1.000
44.031 20.136 11.751 7.851 5.715 4.413 3.556 2.958 2.523 2.194 1.938 1.569 1.318 1.136 1.000
45.053 20.580 11.994 8.001 5.815 4.482 3.606 2.996 2.551 2.215 1.955 1.579 1.323 1.138 1.000
45.830 20.919 12.179 8.115 5.891 4.536 3.645 3.025 2.573 2.232 1.967 1.586 1.327 1.140 1.000
50.984 23.181 13.431 8.899 6.421 4.906 3.922 3.234 2.732 2.355 2.062 1.642 1.357 1.153 1.000
50.981 23.181 13.431 8.899 6.421 4.912 3.922 3.233 2.732 2.355 2.062 1.642 1.357 1.153 1.000
Table. 2. Continued
Jump Characteristics The characteristics of the hydraulic jump in horizontal trapezoidal channel sections represented by some of terminologies will be discussed below. Energy Dissipation Efficiency Hydraulic jumps have been widely used for energy dissipation in hydraulic constructions. Many researchers have paid their attention to them for a long time, (Hashmi, 2003) & (Chaudhry, 2008). The hydraulic jump naturally dissipates energy through turbulence, which can be highly erosive if proper channel protection is not installed, (Hager, 1992). It is therefore preferable, when a hydraulic jump is expected, to control the size and location of the jump in order to localize energy dissipation and erosion, (Stahl and Hager, 1999). The energy loss due to the hydraulic jump is equal to:
∆E = E1 − E2
(25)
With E
=
y +
V 2 2 g
(26)
Where: ∆E: Energy loss due to the jump. E1: Specific energy before the jump. E2: Specific energy after the jump. The ratio of (E2 / E1), represents the efficiency of the jump, (Ef), so: E Ef = 2 E1
Therefore, the relative losses is equal to:
(27)
E ∆E =1− 2 E1 E1
(28)
The difference between the conjugate depths is the height of the jump hj, and the ratio hj/E1, represents the relative height: hj
y2 y (29) − 1 E1 E1 E1 Where: y1/E1: Relative initial depth. y2/E1: Relative sequent depth. It is important to express all the above ratios in term of dimensionless functions of FD1. Depending on Eq.26 and using Eqs.(6 & 10), the relative initial depth could be expressed as: =
y1 2 (k + 2 ) 2 = = E 1 2 (k + 2 ) + (k + 1) F D 1 2 2 + Fr 1
(30)
So, the relative sequent depth will be: y2 y (31) = 1 r E1 E1 Applying Eq.26 at the downstream of the jump, considering Eqs. (14 to 16), results: E2 (k + 1 )3 2 (32) = r + F D1 2 2 y1 2 r (k + 2 )(k + r ) Consequently, from Eqs. (30 & 32), the efficiency will take the following form: E2 2(k + 2)) (k +1)3 2 = xr + 2 FD1 2 E1 2(k + 2)) + (k +1) FD1 2r (k + 2)(k + r)2
(33)
It should be remembered that, the value of r in the above equations, represents the solution of Eq.23a corresponding to the values of FD1 and k1. Since the efficiency and the other relative's definitions become 58
Journal of Environmental Studies [JES] 2012. 9: 53-63
functions of FD1, plotting them against Froude number produces set of chrematistic
curves for various values of k1, see Fig.5.
1.0
Rectangular channel
0.9
E2/E1
k= ∞
0.8
y2/E1
∆E/E1
0.7 0.6
Ratios of characteristics of the jump
Ratios of characteristics of the jump
1.0
hj/E1 y1/E1
0.5 0.4 0.3 0.2 0.1
Traingular channel k=0
0.9
y2/E1
∆E/E1
0.7
hj/E1 y1/E1
0.6 0.5 0.4 0.3 0.2 0.1 0.0
0.0 1
2
3
4
5
6
7
8
9
1
10
2
3
4
5
6
7
8
9
10
FD1
FD1
1.0 Trapezoidel channel k = 5
0.9
Ratiosof characteristicsof thejump
1.0 Ratios of characteristics of the jump
E2/E1
0.8
E2/E1
0.8
y2/E1
∆E/E1
0.7
hj/E1 y1/E1
0.6 0.5 0.4 0.3 0.2 0.1 0.0
Trapezoidel channel k = 40
0.9
E2/E1
0.8
y2/E1
∆E/E1
0.7
hj/E1
0.6
y1/E1
0.5 0.4 0.3 0.2 0.1 0.0
1
2
3
4
5
6
7
8
9
10
1
2
3
FD1
4
5
6
7
8
9
10
FD1
Fig.5: Characteristic curves of the jump in trapezoidal channel sections for varies k1.
The figure indicates that the maximum y2 / E1 always occurs at FD1 = 1.73, independent on the shape of the section k1, within a range of 0.874 to 0.8 for (k1 = 0 to ∞) respectively, giving a maximum value in triangular shape. The maximum hj / E1 is always at FD1 = 2.78, independent on the shape of the section k1, within a range of (0.4 for k1 = 0 to 0.5 for k1 = ∞), giving a minimum value in triangular shape, see Fig. (6). Also, since E1 increases when FD1 increases, the relative height hj/E1 tends to decrease when FD1 increases. However, it should be noted that the decreasing of hj/E1 does not mean a decreasing of y1 or y2 which are expected to increase due to the increasing of the discharge at the higher FD1. 0.6 0.5
K1 = 0
k1 = 5
k1 = 10
k1 = 20
k1 = 40
Rect.
hj / E1
0.4 0.3 0.2 0.1
y1 Yc = = E1 E min
Yc (34) Vc 2 Yc + 2g Where Vc is the critical velocity. The criteria of critical flow condition is, (Chaudhry, 2008). Vc 2 D = 2g 2 Or
y1 Yc Yc = = D E1 E min Yc + 2
(35) (36)
From the background of the hydraulic channel, the hydraulic depth D, is equal to (y and y/2) in rectangular and triangular sections respectively. Hence, Eq.36 provides a value of (2/3) and (0.8) in rectangular and triangular sections respectively. Furthermore, consider Eqs. (8 & 9) for the hydraulic depth D in trapezoidal shape, Eq.36 could be expressed as:
0.0 1
2
3
4
5
6
7
8
9
10
FD1
Fig.6: Relative height of the hydraulic jump for various trapezoidal channel shapes, k1.
Fig.5 shows that the value of y1 / E1 at FD1 = 1, is equal to 0.67 for k1= ∞ and 0.8 for k1=0, while it varies from 0.67 to 0.8 for trapezoidal sections. These results could be explained as follows: When FD1=1, the upstream depth y1 is a critical depth (Yc) and consequently E1 reduces to the minimum specific energy Emin. Therefore:
y1 Yc 2k + 4 = = E1 E min 3k + 5
(37)
Which also indicates that in case of a trapezoidal section, the ratio YC /Emin is between 4/5 for a triangular shape (k1=0) and 2/3 for a rectangular shape (k2= ∞), while it depends on the values of k in the other shapes of trapezoidal section. So, Eq.37 could be considered as a general formula to estimate the value of Yc/Emin in trapezoidal section corresponding to the section ratio k1. 59
Journal of Environmental Studies [JES] 2012. 9: 53-63
due to the increasing of the efficiency where the flow losses the most energy through the jump when FD1 > 6, (steady or strong jump). At the same time, the sequent depth is still increasing, note Fig.2. Consequently the remaining specific energy after the jump is essentially due to the sequent depth y2. Therefore, when FD1 > 6, the velocity head after the jump could be neglected and the specific energy will be estimated by the sequent depth only. In other words, E2 = y2 for FD1 > 6. 0.35 k1 = 0
0.30
k1 = 5 0.25
E2/E1 - y2/E1
Fig.7 shows the efficiency of the hydraulic jump in trapezoidal channel sections. The figure indicates that the section ratio k1, has insignificant effect when FD1 is less than 3. Also, when FD1 is grater than 10, the efficiency sustain at a constant value in a range of 73 to 80 percent corresponding to k1-value. However, in spite of that the rectangular section has a minimum efficiency corresponding to the other sections; the other shapes do not increase the efficiency higher than ten percent, which is insignificant value comparing to the difficulties of the constructions of a triangular or trapezoidal channel. Hence, practically speaking, the rectangular section could be considered more suitable section in the design of the energy dissipation structures.
k1 = 10 0.20
k1 = 40
0.15
k1 = ∞
0.10 0.05 0.00 0
1
2
3
4
5
6
7
8
9
10
11
FD1
Fig.8: The effect of FD1 on the specific energy sequent depth relationship.
100% k1=0
90%
k1=5 80%
k1=10 k1=20
(∆E) / E1
70%
k1=40
60%
Rect.
50% 40% 30% 20% 10% 0% 1
2
3
4
5
6
7
8
9
10
F D1
Fig.7: Relative losses of the hydraulic jump for various trapezoidal channel shapes, k1.
Hydraulic jump length The length of the hydraulic jump is generally measured to the downstream section at which the mean water surface attains the maximum depth and becomes reasonably level, (Philip, 2006). The length of the hydraulic jump is typically obtained from empirical functions of the jump height, based solely upon experimentation (Sturm, 2001). and the location depends on both the length and height of the jump, as well as, the upstream and downstream water surface profiles Chow (1994). Mohd (2008), drove the following differential equation to determine the jump ordinate H at known values of n, H2 and Fr1.
The analysis indicates that in case of FD1 > 6, the efficiency curve (E2/E1) tends to be asymptote to the sequent relative curve (y2 / E1), independent on the section factor k1, see Fig.8. Also, the figure shows that when k1 is grater than 10, the curves join together to a constant value for all values of FD1. This fact could be explained as follows: Based on the results of the Fig.7, the velocity after the jump is always decreased 2 1 (1 + n)(1 + nH2 + n)(1 + 2nH ) ∂H (1+ n) H −1+ (1+ n) H + 1 H (3 + 2nH ) − (3 + 2n) = 1 − 2 2 ∂ξ (1 + nH ) (1+ nH ) 3Fr12 2(1+ nH) 2H (1+ nH) H (1 + nH2 )(1 + nH ) H2 Also, AFZAL (2002). developed the x With n = 1 and ζ = (38) following model to express the length of the 2k ε y 2 hydraulic jump (Lj) in trapezoidal channel where sections. ε : universal constant for eddy kinematic Lj viscosity, independent of channel geometry. (39) = ε (1 − α ) ∆ y2 ζ : non-dimensional constant (= x /ε y2). 2 H: ordinate of jump profile (= y /y1) 4K1 K 2 ∆ = H2: sequent depth ratio (r = y2 /y1) f (ω m ) + B (39 a) (7 +32α + 41α2 +32α3 + 7α4 )M3 +12α(1+α)3 M2 (39 b) In this study, the solution of Eq.38 was f (ωm) + B = 2 / 4 2 3 provided using Runge-Kutta method to +α (41+ 74α + 41α )M +18α (1+α) determine the length of the jump at known (39 c) K 1 = M (1 + α ) + α values of k1, r and Fr1, see Fig.9. 60
Journal of Environmental Studies [JES] 2012. 9: 53-63
With M =
zy1 1 , α = 1 and ε ≈ 2 .578 = r b k1
(39 e)
Fig.9 explains a comparison between the results of Eqs. (38 & 39) and the experimental work of USBR for rectangular section and (Argyropoulous, 1961). for triangular section. The comparison shows that the results due to the model of Eqs. (39) are more precise and applicable than the results of Eq.38. Hence, the model of Eqs.39 was considered here to estimate the length of the hydraulic jump in trapezoidal channel. 9
> 4), the relation will be decreased asymptotic to a constant value, see Fig.12. That means, the maximum ratio (Lj /y2), is always near a section ratio of k1 ≈ 3 to 4, independent on the Froude number FD1. Therefore, for purposes design it is recommended to avoid this ratio in order to minimize the jump length. 13 12 11 10 9 8 Lj / y2
K 2 = 2 M (1 + α + α 2 ) + 3α (1 + α ) (39 d)
7
k1=3
6
k1=1
5
k1=0.5
4
k1=0
3 2 1 0 0
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
FD1
Fig. 10: Hydraulic jump length-Froude number relationship for k1= 0 to 3.
7 12
Eq.38, Rect. Eq.39, Rect. USBR, Rect. K=0, Eq.39 k=0, Argy.
3 1
-1
11 10 9 8 Lj / y2
Lj l y2
13
5
7 6
k1=3
5
k1=5 k1=10
4
1
2
3
4
5
6
7
8
9 10 11 12 13 14 15 16 FD1
Based on the model of Eqs.39 and depending on the solutions of Eq.18 in Table 1, the length of the jump in trapezoidal channel sections were estimated and the results prepared in the dimensionless charts of Figs. (10 & 11). The charts show that for a large value of FD1 the jump length Lj /y2 is independent on the upstream Froude number neither less the value of k1. For the rectangular shape, the results indicate that when FD1 reaches to a very high values, the jump length Lj/y2, is practically constant at approximated value of 6.9. This is because in case of a rectangular shape where M = 0, Eq.39a reduces to ∆=2.667. Consequently the term (ξ x ∆) in Eq.39 becomes 6.9. At the same time when FD1 approaches to infinity, r approaches to infinity too and α = 0 , which makes Eq.39 to give 6.9. It should be said that (Subramanya, 1998). and (Elevatorski, 1959). proposed the constant 6.9 but for FD1 > 5. In this study, when FD1 = 5, the jump length Lj /y2 is about 5.83 which indicates a difference of 17 percent. Also, the results indicate that for a constant Froude number FD1, the jump length ratio is proportional with the section factor k1 until a value of k1 between 3 to 4. After that (for k1
k1=40
2
k1= 60 k1= 100
1
Rect.
0 0
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
FD1
Fig. 11: Hydraulic jump length-Froude number relationship for k1= 3 to ∞. 13 FD1=20 FD1=15 FD1=10 FD1=5 FD1=2.77
12 11 10 Lj/y2
Fig. 9: Results of Eqs. (38 & 39), Comparing with other experimental works.
k1=20
3
9 8 7 6 5 4 0
5
10
15
20
25
30
35
40
45
50
55
60
Section Ratio, k1
Fig. 12: The effect of the section ratio k1, on the maximum length of the hydraulic jump.
Conclusions Applying the momentum conservation across a hydraulic jump in trapezoidal channel sections produced a general fourth order polynomial equation which provides a conjugate depths ratio of arbitrary cross sections. The solution was provided using Newton-Raphson method, and the results are represented as a dimensionless charts and Tables. When the values of the upstream Froude number FD1, are less than 2, the differences between the conjugate depths ratios have low significant change for all the shapes. The maximum values of y2 / E1 and hj / E1 always occur at FD1 = 1.73 and FD1 = 2.78 respectively, independent on the shape of the section (k1). When FD1 is greater than 61
Journal of Environmental Studies [JES] 2012. 9: 53-63
6, the velocity head after the jump could be neglected, (i.e. E2 = y2). The type of cross section has a little effect on the values of FD2 for FD1 > 2 and insignificant effect when FD1 is less than 2. The minimum values of FD2 for all sections range from 0.1 in triangular section to 0.15 in rectangular section, which is insignificant range. Even though, the energy dissipation efficiency of the hydraulic jump indicates that nonrectangular sections are more efficient in high Froude numbers, but these sections produce longer jumps, stability problems, and difficult in constructions. Therefore, from the hydraulic and structural point of view, the rectangular section is the preferable one in the design of hydraulic structures. Moreover, neither less of FD1, the maximum ratio of jump length (Lj / y2), always occurs when the section ratio is about k1 ≈ 3 to 4, which is recommended to avoid that for no longer jump. Nomenclature A1 & A2: Cross-sectional area before and after the jump, respectively. b: Bottom width of the sectional area. k: section ratio E1: Specific energy before the jump. E2: Specific energy after the jump Ef: jump efficiency Emin: Minimum specific energy. F: Specific force Fr: Froude number in term of the depth of flow y. FD: Froude number in term of the hydraulic depth D = A/T. g: Gravity acceleration force. H: ordinate of jump profile (= y /y1). H2: sequent depth ratio (r = y2 /y1). Lj: the length of the hydraulic jump Q: Flow rate r: Conjugate depths ratio of the initial and sequent depths, (y2 / y1) . T: Top width of the sectional area. V: Mean velocity. y1/E1: Relative initial depth. y2/E1: Relative sequent depth Yc: Critical depth. z: side slope ZC1 & ZC2: Distances of the centroids sections from the free surface area before and after the jump, respectively ∆E: Energy loss due to the jump.
ε : universal constant for eddy kinematic viscosity, independent of channel geometry. ζ : non-dimensional constant (= x /ε y2). References Argyropoulous, P.A., "The hydraulic jump and the effects of turbulence on hydraulic structure: contribution to research of the phenomenon". Proc. IX IAHR Congress, Dubrovnik, pp. 173-183., (1961). Noor Afzal & A. Bushra, "Structure of the turbulent hydraulic jump in a trapezoidal channel", Journal of Hydraulic Research, Vol. 40, (2002). No. 2. Chow, V.T., "Open channel hydraulics", McGraw-Hill, New York., (1994) Chadwick, A., Morfett, J. and Borthwick, M. (2004). "Hydraulics in civil and environmental engineering", 4th Ed. Spon Press, London. Chaudhry, Z.A. "Energy dissipation problems downstream of jinnah barrage", Pak. J. Engg. & Appl. Sci. Vol. 3 Jul (2008). (p.19 – 25). M. Hanif Chaudhry, "Open-channel flow", New York, NY 10013, USA, 2nd ed., (2008). Chanson, H. and Montes, J.S., "Characteristics of undular hydraulic jumps: Experimental apparatus and flow patterns", Journal of Hydraulic Engineering 121(2): 129-144., (1995). Chanson, H., "Bubbly flow Structure in hydraulic jump" European Jl of Mechanics B / Fluids, Vol.26,No.3,pp.367-384, DOI:10.1016 / j.euromechflu. 2006.08.001, (2007). b. Elevatorski, E.A., "Hydraulic energy dissipators". McGraw Hill, New York m,kk, (1959). Hager, W.H., "Energy Dissipators and Hydraulic Jump". Kluwer Academic Publishers, Dordrecht, The Netherlands, (1992). Hashmi, M.Z., M.Sc Thesis, "Analysis of Hydraulic Jump and Effectiveness of Energy Dissipation Devices at Jinnah Barrage", Center of Excellence Water Resources
62
Journal of Environmental Studies [JES] 2012. 9: 53-63
Engineering (CEWRE), UET, Lahore, (2003). Hotchkiss, R.H., Flanagan, P.J. and Donahoo, K., "Hydraulic jumps in broken-back culverts." Transportation Research Record, 1851 35-44, (2003). Joe, D. Hoffman, "Numerical methods for engineers and scientists", 2nd ed., New York, Marcel Dekker, (2001). Modi, P.N., "Irrigation water resources and power engineering", 6th, (2004). Mohd Jamil & S A Khan, "Theoretical study of hydraulic jump in trapezoidal channel section", IE (I) Journal-CV, Volume 89, May (2008). Montes, J.S., "Disscusion of undular hydraulic jump, by V.M. Andersen", Journal Hidraulics, Division ASCE 105 (HY9): 1208-1211, (1979). Murzyn, F., and Chanson, H., "Free surface, bubbly flow and turbulence measurements in hydraulic jumps" Report No. CH63/07, Div. of Civil Engineering, The University of Queensland, Brisbane, Australia, July, 113 pages, (2007). Philip, L. Thompson and Roger T. Kilgore "Hydraulic design of energy dissipators for culverts and channels", National Highway
Institute, Technical Report, Third Edition, july, (2006). Roger Reinaur and Willi H. Hager, "Nonbreaking undular hydraulic jump", Journal of Hydraulic Research, vol.33, No.5,p.p. 683-698, (1995). Subramanya, K., "Flow in open channel". Tata McGraw Hill, New Delhi, (1998). Stahl, H. and Hager, W.H., "Hydraulic jump in circular pipes." Canadian Journal of Civil Engineering, 26 368-373, (1999). Sturm, T.W., "Open channel hydraulics", McGraw-Hill, New York, (2001). Treske, A., "Undular bores (Favre-Waves) in open channels. Experimental studies", J. Hydr. Res., 32 (3), 355370, (1994). U.S.B.R., "Hydraulic design of stilling basins and energy dissipators. Engineering Monograph" No. 35, U.S. Bureau of Reclaimation, Dept. of Interior, Washington D.C., (1958). Vatankhah, A.R. and Kouchakzadeh, S., "Discussion of solution of specific energy and specific force equations" by Amlan Das. Journal of Irrigation and Drainage Engineering, ASCE 133(4): 407–410, (2008).
ا ا
"ة ا رو ا ا ف# ا$%& دق ن.د &$' * ) ه" ا/ "# ا$ آ/ ا ا
: ا $=@ذ> رA ق3B) ا: ف وD'7 اEF3 ا-. $;$"رو$#ة ا123 ا456 7* و9$: ): ،+'ا ا, ه-. دMKN ( فD'7 وا+L ,9$F ) فD'7 اEF3ت اKI E$ $;$"رو$#ة ا123 ا95 بHB :@$A 3Q F@اN ا"دي و9 اOM دMKN -= @ذج اT5) ال ا@ل وا: "3 .)61 '"أ اOM (r = y2 / y1) $;$"رو$#ة ا123 ا-3M ' A $N *H ا$': ت: >"اول و-. T5ض اM ): . س.را (FD1 and FD2) ة123" اN و9'* ود. )*) ر$* $N *H وا،*F اX$7: -. ة123ءة ا2 آZ,ود وآ. )*) ر$*و OM دMKN $;$"رو$#ة ا123@ل اQ $\: ): -= ا@ذج اF@اN .(k=b/zy) EF3 ا9 E"ى وا _$ EF3 ا9;B إنT5 اX$N "3 .]( أk=b/zy) EF3 ا9 E( و"ى واr = y2 / y1) ة123 ا-3M ' A ;@ن: +L ا9;7 ا-. 7* اF) إن اb اOM *F اX$7: -. $;$"رو$#ة ا123ءة ا2 آOM @ $`a: D "م3 -. ود. )*" ;@ن رM ة123ة ا6h -. M ;ن إهل اfN .$ اFD1 )$* I -. %١٠ "ودN Lأآ (Lj / y2) ة123" اN k اOة إ123@ل اQ ' A ن. ٣ "ودN EF3 ا9 " ;@نM .٦ -M أFD1 ة123ا اT5 اAر3 "M . FD1 ة123"م ا3 -. ود. )* ر$* OM " $b D:@ OM أO إ9 .تH اE$> -. "ا >"ا$> 3.@ا: l]:ى ا6 أ$M دراتT5A E -= ا9ا@د 63
Journal of Environmental Studies [JES] 2012. 9: 65-72 Original Paper
Morpho-Anatomical Characteristics of Olive (Olea europaea L.) Trees Leaf as Bio-indicator of Cement Dust Air Pollution in Libya A. A. El-Khatib1, D. E. M. Radwan1, A. A. Alramah-Said2 1 2
Department of Botany, Faculty of Science, Sohag University, Egypt. Department of Botany, Faculty of Science, Al-Jabal Al-Gharbi University, Libya.
Rec. 4 Nov, 2012 Accept. 23 Dec, 2012
Abstract Comparisons were made between the anatomical and morphological changes in olive tree leaves from a site with relatively clean air (Al-Khadra area), and two sites (al-Khums and Zelatin) near to cement factories in the area east to Tripoli, Libya. Olive tree leaves exhibited marked variations in their morphological and anatomical characteristics, in relations to variations in the site cement dust air pollution load. Under high pollution load, leaf visible injuries were recorded. In addition, stomata appeared in higher density and smaller size than those of control. The anatomical characteristics of olive leaf including cuticle, epidermis, palisade tissue, mesophyll tissue, and elements of vascular cylinder (xylem and phloem) reflected the deteriorate effects of cement dust air pollutants, the subject which recommend their using as bio indicators. Keywords: Olea europaea, epidermis, stomata, xylem, morphology, cement dust. Introduction Cement dust results from the grinding of a clinker, which is produced by burning a mixture of limestone, clay, and gypsum at high temperatures (1450–16001C) in specially designed kilns (Suess et al., 1985). A cement industry offers an excellent opportunity for studying the impact of dust, during the process of cement manufacture considerable amounts of dust are emitted from handling, spillage and leakages. Dust is produced from quarrying of the major raw material limestone and ending with the packing and dispatch of cement from the industry (Abdul-Wahab, 2006). Cement dust is a gray powder with an aerodynamic diameter ranging from 0.05 to 5.0 mm (Kalacic, 1973). Cement dust can cause illness by skin or eye contact as well as inhalation. Risk of injury depends on duration and level of exposure and individual sensitivity. Moreover, different cements have different ingredients. Many of them contain substances that can be hazardous, like crystalline silica (quartz), lime, gypsum, nickel, cobalt, and chromium compounds (Green N8 Residents Group, 2004). Inhalation of silica dust can cause silicosis or other potentially fatal lung diseases. In addition, inhalation of chromium compounds
found in some cement dusts can cause cancer. Hence, cement dust can be an important pathway for potential human exposure. High concentrations of particles emitted from cement plant may affect the health and property of homeowners living adjacent to the plant. There are numerous complaints about cement plant from nearby residents. They include specific problems about odors, blasting, noise, respiratory problems and corrosive dust on cars. Plant physiological parameters have been used as bio-indicators of urban habitat quality. For example, highly alkaline dustlike cement visibly injures plant leaves; even chemically inert dust physically affects photosynthesis and transpiration when it accumulates on leaf surfaces. Covering and plugging of stomata (Ricks & Williams, 1974). shading (Peirce, 1910; Thompson et al., 1984). increasing leaf temperature (Eller, 1977; Borka, 1984). and removal of cuticular wax (Eveling & Bataille, 1984; Eveling, 1984). had been used to characterize local air pollution (Moraes et al., 2002). Less attention has been given to morphological and anatomical parameters of plants as indicators of long-term responses to changing (urban) habitat quality, although parameters as specific leaf area, stomatal density and pore surface were recognized to * Corresponding author: Dr. A.A. El-Khatib
[email protected]
65
Journal of Environmental Studies [JES] 2012. 9: 65-72
vary depending on microclimatic conditions (Barber et al., 2004). Moreover, sampling and analysis of these parameters are relatively easy and inexpensive. Trees act as a sink for air pollutants and thus reduce their concentration in the air especially in urban environments (Woo and Je, 2006; Tewari, 1994; Rawat and Banerjee, 1996). Dust interception capacity of plants depends on their surface geometry, phyllotaxy, and leaf external characteristics such as hairs, cuticle, leaf shape and size, texture, length of petioles, and canopy of trees etc., weather conditions and direction and speed of wind and anthropogenic activities (El-Khatib, 2007; 2011; Santosh and Tripathi, 2008). The olive tree (Olea europaea L.) is one of the major crops in the Mediterranean region. Whilst its cultivation has spread to other regions around the world, olive production is of vital importance to the economy of Mediterranean countries, including Libya. The marked reduction in the growth and yield of olive trees in the polluted area may be explained in terms of the shading effect of the foliar cement crust as well as through the changes in soil characteristics that had been brought about by the cement factory effluents. Thus the uncontrolled emissions of a cement kiln can affect the growth of the adjacent vegetation through both the air and the soil (Khalid et al., 2009). This paper was to investigate the feasibility of using the changes in anatomical of olive tree leaves in the studied areas as bio-indicators for cement dust air pollution. Materials & Methods The study area: Three sites located in Libya were chosen for the purpose of this study. They were coastal cities located east of Tripoli, their names are Alkhums (Site I) (latitude 32º 38" N and longitude 14º 13" E), Zliten (site II) (latitude 32º 25" N and longitude 14º 29" E) and Al-khadra (Site III) (latitude 32º 26" N and longitude 13º 42" E). The two first sites are located at distance of 0.5 km from the cement factories, while the third one is located far from any pollution sources (distance of 40 km) and considered to be as control. These sites covered by olive trees as main crop, besides fragment vegetation of vegetables and wild species. As reported by
Libyan National Meteorological Center Climatologically Department, (2009), the temperature of this area is ranging between 14.66°C and 25.36°C. The annual mean of wind speed is 6.88 knots/hour, the annual mean of relative humidity is 73.17 %, and the annual mean of rain fall is 24.81 mm. Sampling At each site, leaf samples were collected from olive trees growing around the cement factories at site I and Site II, in four directions to cover the different directions of the plant load emissions as: location (1): west of the factory; location (2) north-west of the factory, location (3) south of the factory, and location (4) south-east. Sampling collection was during summer of 2010 and winter of 2011. At each location, three samples of olive tree leaves were collected, resulting in 12 leaf samples for each study site. Sampling conducted according to Lau & Luk, (2001) method. At each site, by wearing polyethylene gloves, 36 leaves were detached from each tree at 1.5-2 m above the ground by pruning shears from the outer part and inner part of the canopies and from the four directions for the tree (E, W, N, S; nine leaves per each space direction) kept in plastic bags, placed in icebox, and transported to the laboratory for the next preparation. Anatomical investigation To study the leaf anatomical structure of the studied trees, leaf samples were fixed in FAA (formaldehyde: acetic acid: alcohol, 5: 5: 90, respectively) then preserved in 70% ethyl alcohol. Transversal sections (7 µm) were obtained using microtome. The sections were stained with safranin. (0.5gm/500 ml ethyl alcohol) for 30 minutes and washed by different concentrations of ethyl alcohol (50%, 70% and 95%) then the sections stained with light green (0.5 gm/1000 ml ethyl alcohol) for 30 seconds followed by washing with 95% ethyl alcohol .The sections were mounted in canada balsam, dried at 55-60°C for 3 days and examined under light microscope (Olympus-BX51) for description of anatomical structures .The sections photographed by digital camera (Olympus –DP12) and measured by ImagePro Plus 6.1 (Ruzin, 2000).
66
Journal of Environmental Studies [JES] 2012. 9: 65-72
Polluted sites Control
Plate.1. visible injuries show that chlorosis, yellowish, necrosis and drying on the upper surface of leaves, collected from polluted sites (I and II) and control site (III) during summer and winter seasons.
Statistical Analysis: Data were subjected to statistical analysis using Minitab®14. Comparisons of means were carried out using the analysis of variance (MANOVA, Two-way). Differences were considered to be significant at level P?Mا&L
h" :١ K+Tا'1ت ا';)* J 1\F,رة اh
ا Uوا>O ) *R10Gا;Tا و *d *R10Gا X.وا'ء -ا- ا % @G !,ا 1,lت ا';)* " ا ل اFاري%,G ، ' *1ا hوء " ج ز , [)C 1آ[ و%, ا hوً `O; .ا ٥١٠٠ *1'?) X.ام \G %Vف إo1 آ' " *1ا'ء )'Tار ٢٠٠٠ام "` ا',/aار '*1 ا hا1وي أVء ' *1إ *Oا'ء '` وث @,?Gت * " ا X.وا ' ،J.," 1d ! [+Fإن ,ة *Oy) a ا;?G hن ) ٣-١ 1د .*T1Cأن ' *1ا %,G hأو ً ا'ء إ! ا;+F X.ل ! ا;Tام ا*h /1T ا' ،*1أ" * اh,/ام ا'\ت ا *11آ, " %,1ج ا `" ,ا;+) X.رة 1ة )ون إ *Oا'ء ' *-J.ا %V 1hاء ) *Oyا'ء Gر 1.وا hوً، %,G W1إ *Oا'\ت ا) *11ا;C ،,ر از، Jرة ا ،hا?ؤو Y ! *1 [? (1و)- 24
X *d .٤K+Tو"ء "` إJ *Oرة ا[?L ! h ";;Lر
X *d .٥ K+Tو"ء "` إ;C *Oر از ! ;L;" [?Lر
Journal of Environmental Studies [JES] 2012. 9: 21-28
ا 4, 3ا وا (#ت ا : #ا 2#30ء: 'J XF %Gذج ا X.ا1T *Qhس "Tو"* اFJaء 1,TJ load [' 1-G Eو;?Gن ا' *-ا*1+ ) 1ا' %/ ٤٠ -و %,ا %/ ٢٠ *-" ! [1'F, ا' -اNي * ا;',ج .%/ ٥وه YNا19,G %1T -ا XFاNي .1/ي ) %G T J-' *-إh,/ام إ;/اJت Qة ا'ن و);ل "-وي ض اT \'ن +Gف ه YNا;Tا آ''\ *1-) J-ن ;Gز` ا ! ['Fض ا;+) Tرة "-,و*. #ا J 3Zط: ?" XF %Gت ا X.ا1T) *Qhس "Tو"* ا9\Jaط ;C 1-G Eى ";Fر* "Lة ! P/ا';ذج );? W1Fن و 0ن "@)T,ن ا! ;Cى ا9\Jlط و %,إ اء XFا9\Jlط )h,/ام 0ز "Tو"* ا9\Jlط.
;'J .٨ K+Tذج اXF
.٩ K+Tا *1و 0Oدا [dا0.ز
;'J .٦ K+Tذج ' XF [HاFJaء
#ال ا#اري: %Gإ اء XFا ل اFاري 'ذج -ا';ا*Q اFاري ا ل )0.ز اا*1C ا*1/1T ThermoinsulatingواNي Q " be,وق d " [1,-أ)د o) `O;G %/ (١٠×١٠×٥٠) Yا;?G *1ن ! `)" [?Lو) %/ ٢.٥ z'-و"-ة " ا1J. ) 1G19Q 1,1d 1,Tو 0ز ) " oدوج اري );,-"Vن( د ٢ا_ول اف [Cا) *1إدdل( وا JHاف ) ا) *1إdاج( 1Tس ا) 19,ر * اFارة )آ' "; *FOا_?Lل ٧و ٨و ٩أد ،(YJوC Nde) 'Cة Cاءات *1ا;اة '@&* اق در * اFارة W1 ،أNdت أول Cاءة )ء ا; UCو" %V ;?Gن ا,ة ) 1آ[ Cاءة ١٥د.*T1C
0 .٧K+Tز XFا ل اFاري
25
ا 4 2وا :? 2 Ve,ا ل اFاري )?[ آ *-) 1ا'ء إ! اX. )ا;Tام ا (/1Tو *1;Jا'دة ا'\* و 0,-Jو)*T ا *R10G hا'ذج ،إذ إن ا دة *-Jا'ء إ! اqG X.دي إ! GاR .ت )\ 0ا mوGك ات ) hG 01ا'ء "' qدي إ! إhJض ا ل اFاريN ،ا .ا *-) %?F,ا'دة ا'\* @, هNا اhJlض .إن إ *Oا'ء إ! ا X.ا " b+ );F, (CaSo4. ½ H2Oل إ! Rت (CaSo4.2 ) *1 V P+, H2Oآ *,ا';ذج ',/l *.1,J *Qار* ;?Gن ا;رات ا *)lو W1 0?)Gداد ز" ا; ;) z/',د ا'دة ا'\* ) ،دة *-Jا'دة ا'\* داد ز" ا *-) z/',أآ _ [CG 0Jو;Qل ا'ء إ! ا;رات و ;?G dqGا?* ا;ر* ا ًQ;+d *)lإ*O ا?ؤو 1اhم [+1ز" ا X. z/',إ! ٢٨د.*T1C إ اء اام ا ا و ا ت #ادة ا و ا .آ)* )('& اام ا ا %٦٨.٥٥ا،1 و => :8ز;دة ) 2اء إ 3ا ا ا .أ :? #إ9 4داد 78إ6(#ص ا 'ء ) -ا *1)Tاh *1م ا?ؤو+,"l 1ص ا'ء. XF %Gا ل اFاري إ *Oا?ؤو ،1ا،, ;Cر از و Jرة ا hو) -ا;ز،١٠، ٥ ،٣) *1J *h *-J % (١٥ا_/س " ا X.وا'ء ،آ' "*1 ا_(١٧ ،١٦ ،١٥ ،١٤ ،١٣ ،١٢ ،١١ ، ١٠) [?L وا PO;G ,أن ) دة *-Jا'دة ا *11ا'\* أU زدة ا ل اFاري *-Jإ! ا *hا_/س ا*1/1T و 0wهNا وا ًFOاh,/ام Jرة ا hوا ,و ;Cر از ،أ" إ *Oا?ؤوy 1ن ) -ا*1T أ Uزدة ا ل اFاري أآ " Hا'\ت ا_dى )ا;C ،,ر از و Jرة ا,' oJ_ (hز )Tان "ء ا;,ر واNي ?[ G " %15 ًTGآo"G o1
Journal of Environmental Studies [JES] 2012. 9: 21-28
ار ،إ aإ oJآ' زادة o,-Jإ! ا *hا_/س [Cا ل اFاري وذ;?G *C -) zن ا?* ا ً' ،*)aإن ز" ا *h z/',ا_/س X.ه; ٥د E Cو إ *Oا?ؤو ٣ *-) 1و ! % ٥ا;,ا زاد ز" ا z/',إ! ١٥د ،*T1Cوإن ا'& 0اhر 1ت اX. ) إ *Oا?ؤو 1آ;) UJن ا) .m1و" ا*1 ا+,Caد* ن آ* ا X.ا' *Oy) -Fا?ؤوo1 1 زدة *1CوT" *1 ,Gر `" *Jا -F,ا';Fظ *1;Jا `1' X.ا;hاص. درا */و [1FGاQ;F x ,ت ا;d 1G ,اص ا ل اFاري إJ *Oرة ا hإ! *dاX. ; إن إJ *Oرة ا hإ! ا*1)C " X. oاFاري ،إ aإن زدة Jرة ا*1 -) h qدي إ! *1)C [1TGا X. [19,اFوي ! Jرة ا *1)C -) *1 -) hا"+,ص 'ء ) .دة ";,Fى Jرة ا hاqG X.دي إ! زدة ز" ا +,ا_ 0ن ه YNارة ;,FGي ! ا وا?-ت وا;1-ز وا? 1وا 1,وا! VqG , ' *1ا_"ه oو " Xh,هNا ا 1Ve,ا\ر e.Jإ! ا' *.ا' *T-رة ،أ" ز" ا +,ا,)aا [T oJy ); ;د ارة _ X,'G 0Jءًا " "ء ا .hإن زدة *-Jارة اqG X.دي إ! إhJض *1)Cا[19, "' qدي إ! زدة *-Jا'ء إ! ا;+F X.ل ! *1)Cا [19,ا';ب و? ذ;? zن ! -ب ا'Tو"* .إن "Tو"* ا9\Jaط X.اFوي ! Jرة ا;?G hن " *,إ! " *\hا',دا ! J *-Jرة اT" [TG W1 hو"* ا9\Jaط ) دة J *-Jرة ا .hإن ا X.اFوي ! Jرة ا;?G hن *1d ا;زن N0ا '? اh,/ا"_ 0اض ا ل ا.G;+
XF .١٤ K+Tا ل اFاري '\ت ا%٣ *-) *11
XF .١٠ K+Tا ل اFاري إJ *Oرة ا.h
XF .١٥ K+Tا ل اFاري '\ت ا%٥ *-) *11
XF .١١ K+Tا ل اFاري إ *Oا.,
XF .١٦ K+Tا ل اFاري '\ت ا.%١٠ *-) *11
26
XF .١٢ K+Tا ل اFاري إ *Oا?ؤو.1
XF .١٣ K+Tا ل اFاري إ;C *Oر از
Journal of Environmental Studies [JES] 2012. 9: 21-28
:*11ت ا'رة ا1TG [ و/ "و،1 اb/; ا ام "دةh,/) *1?/ * )ء دار1T1G *).G ،[Q;' "* ا،*1/0* اا ا." ."1ا .٢٠٠٥ ،٢ اد،١٣ ." اb,* ا-J ب زدة/* أ/ "درا، [/) ه */0* ا." ."رh ه );ق ا,هة اwف و.ا ،٤٣٧-٤٢٣ *FQ ،١٢ اد،٢٧ ." ،1 ;;?,وا .٢٠٠٩ 19, ا1VeG */ "درا،%/ 1- و هى1- @م/ ! C ا اا%F اء ا;ري ،1 ;;?,* وا/0* ا." ."*1 )0? اX +hا .٢٠٠٩ ,٦٠٥-٥٩٥ *FQ ١٦ اد،٢٧ ." ،"U1 وا;ر";آU11* ا+ *+' "ا،'F" 'ا :U1J,Ja?* اL ! [1Q, ا.٢٠١٠ http://www.perlite.com ." ااق1* ا);ق اQ" ،;ري. " اV *". ا،ءاتJl* اء وا/د);م ه .٢٠٠٠ ،*1 ;;?,ا _اضX. "ا،٢٨ %C* ر1C* اا1/1T* اQا';ا ،*1;ة ا1- وا11T, ز ا'آ ي0. ا."اء .١٩٨٨ *1 1;ص اF "ا،٢٧ %C* ر1C* اا1/1T* اQا';ا 11T, ز ا'آ ي0. ا." _اض اءX. .١٩٨٨ ،*1;ة ا1-وا Taneja, A. and Killo, F.,, "Development Of Hydrolic Binder Based On Gypsum Plaster”. Building Research Center, Baghdad, Vol. 6, No.2, ppp.50-63, (1987). Doxiad- QBE-5, 5, “Survey of the problems of Juss and Juss production in Iraq”. Building research Center, Baghdad, pp.1 pp.185, (1969). Khairia Al-Ramadani Ramadani and Taneja, G., "Development of Gypsum plaster products for use in buildings”. Building Research, search, R.P. 77/88, pp.37-40, pp.37 (1983). Mohan, R. Manjit, S. “Gypsum as a building material”, Central 32 Building Research, India, No. 14, pp. 1-6, (1983 1983). Malhorta H.L, ”Properties of materials at high temperature”. Journal of materials and structure, Vol. 15, pp. 170, (1982). ISO 3048-74, 74, “Gypsum PlastersPlasters General Test conditions” 1st edition, (1974). (
%١٥ *-) *11اري '\ت اF ا ل اXF :١٧ K+T
: درO ا اضoG"اh,/ ا% واهh "ا،%w آQ %/ ،*1 ;;?,"* ا. ا، د);مWF) ."*1 Jlا .٢٠٠٠ ،;ر-.* اق وا/ه ، ا;هب/ در وT ا,J\"* ا ا1d *1LT* اTF ا." وا;رة اءX.ام اh,/"إ .٢٠٠٢ ،٢ ص،*1C اا1',?ن وا/l;زارة ا ، ا;هب/ در وT ا,J\"* ا ا1d ."(X.* )ا واV_* و ا1 ا';اد اX +d" ت/ راT,د ا' وا/p !* ا_و1;اوة ا ،٢٤ ص،*1Cر* ااN* اC "&'* ا،*V_ا .٢٠٠٠ \ريFاري اء اF "ا ل ا،1` ا/ %أده *Q'ط اء ا; ا) وJ* أJرT"و ،*1) ا' اWF ا." دFG إ."1ا);ق ا .١٩٨٤ ،٢٩٧ -٢٩٢ ص،اد9) ;اصh ا1-FG" ,J'اF[ ا+1 ري واس. اFQ ."*\''ل ا';اد ا,/) اX. *1 1ا ،١ ء،٤." ،"h' ا' اGq';ث اF) ` Cو .١٩٨٩ ،١١٨-١٠٢ ص ;ر وا'دنh+ء ا1'1; آ1 " ،;T ا%?هة اJ ،١٠٢ ص." ااق.` اC ";ا-*1+ا .١٩٧٩ 1-FG" ،J'اF[ ا+1 ر ا و اس1 'F" . " اx,'ص اhع اT اX ;اصd ص،١ د،٧ ." ،;ث اءF) *." ،";يJHا .١٩٨٨ ،١٠٩-٨٥ , "ا- ا;هب ا/ وJ\"* ا ا1d ."ً آ';اد ز* ارX. وا1");ق اء ا ،(* ا';اد/ )هJH اJ* ا_رد1J'* ا/0' اGq" .١٩٩٩ ،٢٥٦-٢٤٥ ص،ا_ردن ;اصd m) 1-FG" ،;ي/;' ا%w! آ/;" [1T *اd تh" ف1* أOy) *1J/hا@ت ا * اء/ ه1,- " * أو."ا'دن .٢٠٠٠ ،*1 ;;?,"* ا. ا،ءاتJlوا
27
Journal of Environmental Studies [JES] 2012. 9: 21-28
Improve Thermal Insulation And Physical Properties Of The Iraqi Plaster Using Natural Additives Abstract Fires are considered to be one of the most common disasters in the buildings at the present time; therefore it becomes necessary to design the buildings with fire-resistant materials. Many types of stucco panels’ fire-resistant material have been created to prevent heat transfer to other parts of the institution, and to protect it from damage, so intensify increased to study how to improve the properties of the Iraqi plaster. Iraqi plaster differs from other types of plasters with its high quality mechanical and physical characteristics and this is because of the purity of its raw materials (rock stucco) and the advanced technology used in the production. However, there are some negative aspects that led to the lack of demand for it and, make it unsuitable for use as a binding agent, such as the lack of resistance to stresses tensile, lack of resistance to moisture and freezing speed leading to a significant loss of plaster during working with it, and thus lead to increased construction costs. In order to improve the properties of the Iraqi plaster many types of natural additives have been used in this research which are; Hay, Rice husks, sawdust and Alcaúlan, with a suitable ratios. The research also include studying the effect of this additives on physical and mechanical characteristic of Iraqi plaster, and studying the effect of the ratios of these additives on thermal insulation of the Iraqi plaster to choose the best additives type and to keep the high quality as possible of the material while maintaining the quality of the material and to make it remains within the standard specifications of plaster for construction purposes. Thermal insulation have been investigated after adding caúlan, Hay, Rice husks and sawdust with addition ratios of;3, 5, 10, 15% by weight of plasters. Results showed that the thermal insulation highly related to the ratio of water to plaster and with the type of the additives material. Increasing the ratio of natural additives led to an increase in the thermal insulation and this appears clearly with sawdust, Hay and Rice husks. While adding only small ratios of caúlan gives the highest thermal insulation bigger than other types of additives, this is because of its characteristic of losing the crystallization water, which constitutes approximately about 15% of its formulation when dealing thermally with it, but whenever caulan ratio increases the thermal insulation decreases due to the obstruction of the needle network formation.
28
Journal of Environmental Studies [JES] 2012. 9: 29-35
Original Paper
Germination of jojoba (Simmondsia chinensis L) seeds under the influence of several conditions Hassanein A. M.1, Galal E.2, Soltan D.1, Abed-Elsaboor K.2, Saad G. K.1, Gaboor G. M.1, El Mogy N. S.3 1
Central Laboratory of Genetic Engineering, Faculty of Science, Sohag University, 82524 Sohag, Egypt. 2 Genetics Department, faculty of Agriculture, Sohag University, Sohag, Egypt. 3 Al Obour Buildings 4, Salah Salem Road, Nasr City – Cairo, Egypt. Rec. 20 Mar, 2012 Accpt. 2 May, 2012
Abstract Our study indicates that jojoba is suitable plant for cultivation of the Egyptian marginal soils, in the desert area, where the seeds were germinated and grown in sandy soil of marginal fertility. To study the effect of NaCl and mannitol on seeds germination, jojoba seeds were placed on cotton layer flooded with solution containing different concentrations of them. Salinity stimulated seed germination, especially, when the seeds were subjected to relatively low concentration of NaCl (0.5 – 3 gm/l). Increase the concentration of NaCl over 3 gm/l resulted in inhibition of seed germination as well as radicle growth. Application of 2 or 3 gm/l mannitol in germination medium improved the seed germination, vice versa was detected under progressive increase of mannitol in germination medium. Mannitol as same as NaCl delayed seed germination of jojoba plant. On the other hand, jojoba seeds can be germinated in low frequency under high concentration of mannitol, up to 100 gm/l, when seeds were placed on three cotton layers just wetted by distilled water containing mannitol. Temperature may be the most critical factor during jojoba seed germination, therefore summer was the best season for seed germination; also, 30 oC was the best temperature degree for seed germination and emergence of radical in the shortest time. Key words: Desert cultivation, Jojoba, mannitol, sodium chloride, seed germination, stress. Plantations are established by using seeds, Introduction: Jojoba [Simmondsia chinensis (Link) seedlings, rooted cuttings, or plantlets Schneider] is a desert shrub which tolerates produced from tissue culture (Roussos et al., salinity and drought. The chromosome 1999; Roussos et al., 2006; Mohasseb et al., number of jojoba is 2n = 52 (Weiss, 1983). 2009). The male plants outnumber the Its natural life span appears to be between females when raised from seeds (Harsh et 100 and 200 years. Jojoba seeds contain a al., 1987). Jojoba plants obtained from seeds liquid wax of economic importance in showed a high variability in most industry (machine lubricant) as well as in characteristics including yield because it is medicine, where it can be used in cosmetics dioecious, and obligate cross-pollinated and anticancer compounds. Jojoba was used species (Gentry, 1958). Previous reports as a medicine for cancer, stomach ache, indicated that only a small proportion of the kidney disorders, easing childbirth and in plant population (less than 1%) originating tending wounds (Weiss, 1983). Jojoba has from seeds of native plants has the potential attracted interest as a landscape plant; also it to produce economically acceptable yields can be sued for soil conservation. The plant (Purcell and Purcell, 1988; Ramonet-Razon, has a deep root system; therefore it can be 1988). Therefore, comprehensive selection used in highway and roadside plantings and and breeding program was conducted in hedges. It can also be used as a soil stabilizer many countries all over the world to obtain in green belts around desert cities suffering elite cultivars. from particulate air pollution. It is the only Salinity is considered one of the most plant known that synthesizes liquid wax. The important factor restrict the horticultural seeds contain about 50% of simple wax production, especially in soils of the arid and esters of mono-unsaturated fatty acids and semi-arid regions on the earth. Few alcohols. economical plant species can be grown * Corresponding author: Dr. Hassanein A.M.
[email protected]
29
Journal of Environmental Studies [JES] 2012. 9: 29-35
successfully in saline soil. It is worth to mention that the total area of arable land is gradually decreasing due to the progressive salinization of the soil (Botti et al., 1998). While jojoba is known as salt tolerant species (Jensen and Salisbury, 1988; Benzioni et al., 1992). salt damage can occur and differences in response among clones had been observed (Rasoolzadegan et al., 1980; Benzioni et al., 1992). indicating the possibility of developing clones with increased levels of salt resistance or tolerance. Elongation and thickening of stems (Bartolini et al., 1991). the total leaf area and leaf size (Bartolini et al., 1991). shoot and leaf expansion, number of leaves and flowers were reduced in response to increased levels of salinity (Rasoolzadegan et al., 1980; Benzioni et al., 1992). Increasing in leaf thickness was also reported when jojba plants were subjected to salt stress (Sa´nchez-Blanco et al., 1991). Benzioni et al., 1999 reported that some clones exhibited excellent vegetative traits related to yield potential such as a high survival rate, rapid growth, extensive branching, high node density, high flower density, high percentage of fruit set, high seed weight, and high wax content in the seed. The clones also differed in their wax composition. Under Egyptian condition, jojoba maximally utilizes 50-70 liters of water weekly in summer and 10-30 liters in winter but when it irrigated by flooding, 1215 irrigation times per year is needed. Mature shrubs characterize by their strong ability to survive without irrigation for long time where they can survive for a whole year without watering. Jojoba can also tolerate up to 3,000 p.p.m. without any impact to the yield. Therefore, Jojoba is considered one of the most practical and scientific solutions for desert plantation in Egypt. In spite of its importance, very few studies aim to understand the effects of abiotic stresses on the development and yield of the jojoba. This article covers the research on jojoba ecophysiology, with emphasis on the effects of water and salt stress on seed germination. Material and Methods: Plant material: For the experiments, seeds were obtained from the Egyptian Natural Oil Co. S.A.E., Ismailia Farm, Salam Zone, Manayef, Ismailia, Cairo, Egypt. The farm is
planted in Ismailia in 1991 and it is about 88,200sq.m of jojoba plants, it was used for research and production. Effect of soil type on seed germination: Thirty jojoba seeds were sown in plastic pots containing two Kg of soils composed from sand, soil or both according to the following table: Soil structure Sandy soil Clay soil 100% 0% 75% 25% 50% 50% 25% 75% 0% 100%
After 40 days percentage of seed germination and germination period were estimated. An emerged radicle was the criterion for germination (Côme, 1982). and the growth of the seedlings was laboratory or greenhouse conditions. Effect of season on seed germination: Thirty jojoba seeds were sown in plastic pots containing two kg of soil containing 1 and 1, sand and clay soil, respectively. After 40 days percentage of seed germination and germination period were estimated. Effect of temperature on seed germination: Jojoba seeds were grown on cotton in glass jars contained 50 ml Hogland solution and incubated at 30°C, 40°C, and room temperature (maximum 18°C). Germination frequency, length of roots, length of shoots and number of leaves per shoot were determined after four, nine, and 21 days of seedling. Effect of NaCl on seed germination: Under sterilized condition, Jojoba seeds were grown on cotton in glass jars contained 50 ml of Hogland solution supplemented with several concentrations of NaCl (0, 0.5, 1, 2, 3, 4 g/l). Jars were incubated at 30°C. Germination frequency, length of roots, length of shoots and number of leaves per shoot were determined after four, nine, and twenty one days of seedling. Effect of mannitol on seed germination: Jojoba seeds were flooded on cotton layer in sterilized glass jars contained 50 ml Hogland solution supplemented with several concentrations of mannitol (0, 0.5, 1, 2, 3, 4 g/l). Jars were incubated at 30°C. Germination frequency, length of roots, 30
Journal of Environmental Studies [JES] 2012. 9: 29-35
length of shoots and number of leaves per shoot were determined after four, nine, and twenty one days of seedling. In addition, jojoba seeds were placed on three cotton layers wetted with 50 ml and containing different concentration of mannitol. The percentage of seed germination was determined in 40 days. Results and discussion: The used jojoba seeds were usually smooth, brown to black in colour, their dimensions are 8 – 17 mm in length and 511 mm in cross-section. One hundred seed weight can vary from 61 - 157.8 gm/100 seed. Positive correlation was detected between seed size and oil content but the quality of the oil was exhibited very little variation regardless of the geographic origin of the seed (Yermanos, 1979). As was reported previously, the seeds contain little or no endosperm and consist mainly of the undifferentiated tissue of the cotyledons (Weiss, 1983). In this work, seeds were obtained after two months of harvesting date and they showed germination when they were subjected for suitable condition for seed germination. They were readily germinated in sandy or clay soil or in mixture from them under wide range of temperature from 18- 40 oC, it was in accordance with others studies (Gentry, 1958; Yermanos, 1982). Data in this work (Table 1) indicated that sandy soil is the most suitable soil for seed germination of jojoba plant, where it is expressed the highest percentage of germinated seeds in short time. Therefore, our study indicates that jojoba is suitable Age of seedling 3 days 5 days 7 days 15 days
plant for cultivation of the Egyptian marginal soils, in the desert area, where the plant can grow in sandy soil of marginal fertility and needs little water. It withstands salinity and it does not seem to need fertilizers or other polluting chemical treatments. Consequently, jojoba can be generally cultivated in well-drained, coarse, desert soils, where the soil is composed of sandy alluviums and mixtures of gravels and clays derived from such igneous materials as granitics and volcanics. For all of the previous reasons, jojoba is recommended for cultivation in Egyptian desert. Soil structure Sand Clay y soil soil
Percentage Germinat of seed ion germination period (%) (day) 100% 0% 75.0 13 75% 25% 65.0 15* 50% 50% 62.5 17* 25% 75% 55.0 21* 0% 100% 45.0 23* Table 1. Effect of soil type on percentage of seed germination and germination period.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution at 30°C at P < 0.05. Temperature may be the most critical factor in growing jojoba. Jojoba is living in the bright desert sun and tolerates the extreme daily fluctuations of temperature which commonly range through -1 oC during the morning to daily extremes of 46 oC (shade readings). In our work, increase of temperature stimulated seed germination, shortened the time needed for emergence of radical (Table 2).
Temperature of Seed germination Length of Shoot incubation freq. root freq. (℅) 30°C 61 0.26 --Room temperature 55* 0.2 --30°C 72 0.4 --Room temperature 55 0.53 --Room temperature 55 2 33 30°C 72 7 66 Table 2. Effect of temperatures on seed germination frequency.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution at 30°C at P < 0.05. Seed germination was influenced by temperature of the seasons. Seed germination in summer was higher than
Length of shoot --------1.5 0.8
winter (Table 3). Summer was the best season for seed germination it may be due to the highest temperature degree. Also, the shortest time of seed germination was detected when the seeds were subjected for the highest temperature in summer. Seedlings are more sensitive than mature 31
Journal of Environmental Studies [JES] 2012. 9: 29-35
tree (Weiss, 1983). While seeding is sensitive to light frosts of -1 or -2oC below freezing, mature shrubs are known to tolerate temperatures as low as -9 oC. When temperatures reach 50C flowers and terminal portions of young branches of most jojoba
plants are damaged. Wild jojoba plants can withstand very high temperature, cultivated cultivars showed maximum growth between 27 - 36 oC, but. Above 50 oC , the vegetative growth is suppressed, although not lethal (Weiss, 1983).
Parameter
Season Summer Autumn Winter Spring 77 ±3.81 63 ±2.00 58 ±3.81 73 ±2.50 Percentage of seed germination 13 ±1.00 17 ±1.00 26 ±2.00 17 ±1.52 Germination period / day Table 3. Effect of seasons on percentage of seed germination and germination period.
Under germination condition, the number of germinated jojoba seeds increased with time (Table 4, 5 and 6). In four days, salinity delayed seed germination of jojoba seed. While, 61% of seeds showed seed germination on NaCl free medium, 57% of seeds showed seed germination under the influence of 0.5 gm/l NaCl (Table 4). With time on germination medium, salinity stimulated seed germination (Table 5 and 6) especially, when the seeds were subjected for germination in the presence of relatively low concentration of NaCl (0.5 – 3 gm/l). In this work, the negative effect of NaCl on seed germination was detected when the seeds were subjected for 4 gm/l NaCl. While jojoba is known as salt tolerant species (Jensen and Salisbury, 1988; Benzioni et al., 1992), salt damage can occur and differences in response among clones had been observed (Rasoolzadegan et al., 1980; Benzioni et al., 1992). indicating the possibility of developing clones with increased levels of salt resistance or tolerance. Relatively low concentration of NaCl (0.53 gm/l) stimulated seedling growth and resulted in the formation of higher fresh mass than control. On the other hand, germination of seeds on medium containing 4 gm/l NaCl retarded seedling growth with complete avoidance of shoots (Table 5 and 6). Elongation and thickening of stems (Bartolini et al., 1991). the total leaf area and
leaf size (Bartolini et al., 1991). shoot and leaf expansion, number of leaves and flowers were reduced in response to increased levels of salinity (Rasoolzadegan et al., 1980; Benzioni et al., 1992). Increasing in leaf thickness was also reported when jojba plants were subjected to salt stress (Sa´nchez-Blanco et al., 1991). Conc. of Germination DRS NaCl (g/l) freq. (℅) Control 61 0.27 0.5 56.6* 0.17 1 38* 0.13 2 55.4* 0.6 3 44* 0.1 4 34.3* 0.1 Table 4. Effect of NaCl on seed germination after four days under germination condition.
* Means significantly different (t-test) from jojoba seeds cultured on hogland solution without salt at P < 0.05. Increase the concentration of NaCl over 3 gm/l resulted in inhibition of seed germination as well as radicle growth (Table 5). Plumules were completely suppressed when 4 gm/l NaCl were used. These results were in agreement with previous report (Berrichi et al., 2010). They were found that 5g/l of NaCl inhibited completely the emergence of plumules and, 3 g/l of NaCl marked the start of negative effect on the growth jojoba seedlings.
Conc. of Germination Length of root Shoot freq. Length of shoot NaCl (g/l) freq. (℅) (cm) (℅) (cm) Control 66 1.7 16 0.5 0.5 61* 5.3 16 0.3 1 66* 3 16 0.4 2 83 11 33* 0.4 3 75 7.25 33* 0.5 4 41* 0.23* ----Table 5. Effect of NaCl on seed germination after nine days under germination condition.
32
Journal of Environmental Studies [JES] 2012. 9: 29-35
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without salt at P < 0.05. Relatively low concentration of NaCl resulted in enhancement of seedling growth up to 3 gm/l NaCl (Table 6). The data also indicated that 4 gm/l of NaCl resulted in decreasing the radical length and inhibition of plumule formation. Botti et al., (1998) reported that jojoba plants grown under high Conc. of NaCl (g/l)
Germination freq. (℅)
salt levels did not show much difference from those grown under non-saline conditions for most of the morphological and anatomical parameters such as number and size of stomata, density of trichomes, leaf size, branching characteristics and stem diameter. On the other side they found that leaf and cuticle thickness showed a high tendency to increase under saline conditions.
Length of root (cm)
Plumule Length of No. of No. of formation shoot (cm) leaves per shoots freq. (℅) shoot per seed Control 69 2 33.3 0.8 2 1 0.5 66.6* 6.66 50 1 2 1 1 66.6* 3* 50 1 3 1 2 83* 15.3 42.2 4 6 1 3 83.3 14.3 33* 2.3 4 1 4 50* 0.73* --------Table 6. Effect of NaCl on seed germination after fifteen days under germination condition.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without salt at P < 0.05. Mannitol as same as NaCl delayed seed germination of jojoba plant (Table 7). Application of 2 or 3 gm/l mannitol in germination medium improved the seed germination. Comparison between the effect of NaCl and mannitol indicated that incorporation of these both factors in relatively low concentration improved seed germination. Conc. of Germination Length of mannitol (g/l) freq. (℅) roots (cm) Control 61 0.27 0.5 46* 0.1* 1 55* 1.8 2 46* 0.46* 3 33* 0.16* 4 27* 0.1* Table 7. Effect of mannitol on seed germination after four days under germination condition.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without mannitol at P < 0.05. The data in this work indicated that the emergence of plumules were commenced after four days of subjecting the seeds for germination conditions (Table 8 and 9). The commencement of plumules was depend on the concentration of mannitol in the germination medium. While relatively low concentrations of mannitol (1 – 3 gm/l) stimulate plumule formation, 4 gm/l mannitol inhibit completely the emergence of seed plumule. The same results were obtained when 4 gm/l NaCl were used (Table 6).
Conc. of Germination Length of Plumule Length of mannitol freq. (℅) roots (cm) freq. (℅) shoots (cm) (g/l) Control 66 1.7 16 0.5 0.5 55.5* 1.15* 16 0.5 1 55* 8.5 50 0.3 2 66* 7 33 0.2 3 83 3.3 25 1 4 50* 0.5* ----Table 8. Effect of mannitol on seed germination after nine days under germination condition.
33
Journal of Environmental Studies [JES] 2012. 9: 29-35
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without mannitol at P < 0.05. Plumule formation were delayed under the influence of 4 gm/l mannitol where it was only commenced in two weeks (Table 9). On
the other hand, in two weeks, 4 gm/l mannitol stimulated the radical length in comparison to that of control. These data indicated that mannitol in concentration between 1 and 3 m/l stimulated both shoot length and the number of shoots per seed.
Conc. of Germination Length of Plumule Length of No. of No. of mannitol freq. (℅) roots (cm) freq. (℅) shoots (cm) leaves per shoots (g/l) shoot per seed Control 66 2 33 0.8 2 1 0.5 55.5* 2 33 0.8 2 1 1 58* 14.6 50 3.16 2 2 2 83 9 33 1.1 2 1 3 83 7.66 83 1.81.8 2 3 4 50* 5.7 30* 0.66 --1 Table 9. Effect of mannitol on seed germination of seeds placed on one layer of cotton flooded with Hogland solution for fifteen days.
* Means significantly different (t-test) from jojoba seeds cultured on Hogland solution without mannitol at P < 0.05. Placing jojoba seeds on three cotton layers just wetted by germination medium created suitable condition for seed germination although the presence of high concentration of mannitol. Under these conditions, jojoba seeds were able to germinate and form plumule up to 100 gm/ mannitol. Comparision between data in tables 9 and 10 indicated that seed germination was strongly Treatment 0 86
10 96
20 86
30 80
affected by the presence of high water content in germination medium. It was expected since the plant strongly tolerates drought condition but it is sensitive for frost and water flooding. Consequently, jojoba has recently established as a crop in many arid and semi-arid regions of the world (Brown et al., 1996), especially around the Mediterranean basin (Benzioni and Dunstone, 1986; Mills et al., 1997) because it is drought and salt tolerant plant species.
Mannitol concentration (gm/l) 40 50 60 70 80 76* 63* 60* 56* 46*
90 43*
100 36*
110 20*
Percentage of seeds cultured (%) 8 7 9 11 11 13 15 16 17 19 21 25 Germination period (day) 18 27* 12* 10* 8* 7* 6* 5* 3* 2* 1* 0 N .of shoot formation Table 10. Effect of mannitol on seed germination of seeds placed on three layers of cotton and witted with distilled water solution for fifteen days.
* Means significantly different (t-test) from jojoba seeds cultured on distilled water without mannitol at P < 0.05. The data of his work indicated that jojoba is the most suitable plant for the Egyptian conditions especially in desert area. Under Egyptian condition, jojoba maximally utilizes 50-70 liters of water weekly in summer and 10-30 liters in winter but when it irrigated by flooding, 12-15 irrigation times per year is needed. Mature shrubs characterize by their strong ability to survive without irrigation for long time where they can survive for a whole year without
watering. Jojoba can also tolerate up to 3,000 p.p.m. without any impact to the yield. Therefore, Jojoba is considered one of the most practical and scientific solutions for desert plantation in Egypt. References: Bartolini, G., Mazuelos, C., Troncoso, A., (1991). Influence of Na2SO4 and NaCl salts on survival, growth and mineral composition of young olive plants in inert sand culture. Adv. Hortic. Sci. 5, 73–76. Benzioni, A., Nerd, A., Rosengartner, Y., Mills, D. (1992). Effect of NaCl salinity on growth and development of jojoba clones I.
34
Journal of Environmental Studies [JES] 2012. 9: 29-35
Young plants. J. Plant Physiol. 139, 731– 736. Benzioni, A, Shiloh, E., Ventura, M. (1999). Yield parameters in young jojoba plants and their relation to actual yield in later years Industrial Crops and Products 10: 85–95. Berrichi, A., Tazi, R., Bellirou, A., Kouddane, N., Bouali A. (2010). Role of salt stress on seed germination and growth of jojoba plant Simmondsia chinensis (Link) Schneider. IUFS J Biol 69:33-39 Botti, C., Palzkill, D., Munoz, D., Prat, L. (1998). a. Morphological and anatomical characterization of six jojoba clones at saline and non-saline sites. Ind. Crops Prod. 9, 53–62. Brown, J.H., Palzkill, D., Whittaker, C., (1996). The jojoba industry 1994, a status and update. In: Princen, L.H., Rossi, C. (Eds.), Proc. of the Ninth International Conf. on Jojoba and Its Uses, and of the Third International Conf. on New Industrial Crops and Products, 25–30 September 1994, Catamarca, Argentina, pp. 150–154. Côme, D. (1982). Germination. In: Mazliak P., ed. Croissance et développement. Physiologie végétale. II. Paris: Hermann, 129–225. El Mogy, N.S. (1999). Egyptian Experience in Planting Jojoba Fourth International Water Technology Conference IWTC 99, Alexandria, Egypt 431. Jensen, W.A., Salisbury, F.B. (1988). Bota´nica, 2nd ed. Libros McGraw-Hill de Me´xico, Me´xico, 722 pp. Harsh, L.H., Tewari, J.C., Patwal, D.S. and Meena, G.L. (1987). Package of Practices for Cultivation of Jojoba (Simmondsia chinensis) in AridZone, Pp: 1–19. CAZRI, Jodhpur (India). Mohasseb, A.H., Mohamed, K., El-Bahr, M.K., Adam, Z.M., Moursy, H.A. and Solliman,
M. (2009). In Vitro Clonal Propagation of Jojoba (Simmondsia Chinensis (Link) Schn.). Aus tralian Journal of Bas ic and Applied Sciences , 3: 3128-3136. Rasoolzadegan, Y., Hogan, L., Palzkill, D.A. (1980). Response of jojoba to five levels of salinity. In: Puebla, M. (Ed.), Proc. of the IV International Conf. on Jojoba, 5–6 November 1980, Hermosillo, Sonora, Mexico, pp. 113– 120. Roussos, P.A., Tolia-Marioli, A., Pontikis, C.A. and Kotsias, D. (1999). Rapid multiplication of Jojoba seedlings by in vitro culture. Plant Cell, Tissue and Organ Culture 57: 133–137. Roussos, P.A., Tsantili, E., Pontikis, C.A. (2006). Responses of jojoba explants to different salinity levels during the proliferation stage in vitro Industrial Crops and Products 23: 65–72. Sa´nchez-Blanco, M.J., Boları´n, M.C., Alarco´n, J.J., Torrecillas, A. (1991). Salinity effects on water relations in Lycopersicon esculentum and its wild salt-tolerant relative species L. pennelli. Physiol. Plant. 83, 269– 274. Weiss, E.A. (1983). Crambe, niger and jojoba. In: Oilseed Crops. Longman, London, UK, pp.507 - 527. Yermanos, D.M. 1979. Jojoba - a crop whose time has come. California Agriculture (Jul Aug.), pp. 4 - 11. Yermanos, D.M. (1982). Jojoba - A potentially valuable species in the control of desertification. Proceedings of the Conference on Alternative Strategies for Desert Development and Management, 31 May - 10 June 1977, United Nations Institute for Training and Research, Sacramento, California, USA. Agriculture Vol. 2, pp. 374 - 381.
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Journal of Environmental Studies [JES] 2012. 201 9: 37- 42
Original Paper
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Journal of Environmental Studies [JES] 2012. 9: 37- 42
Vaboliene, G., Matuzevicius, A.B. and Dauknys, R. (2007). "Impact of temperature on biological phosphorus removal from wastewater in Lithuania" EKOLOGIJA. 2007. Vol. 53. No. 4. 95–101 WPCF, APHA and AWWA (1999) "Standard Methods for the Examination of Water and Wastewater " 20th ed, Washington D.C. USA Zou, H., Du, G.C., Ruan, W.Q. and Chen, J. (2006). "Role of nitrate in biological phosphorus removal in a sequencing batch reactor". World Journal of Microbiology & Biotechnology, 22: 701–706.
Technology Conference, IWTC9 2005, Sharm El-Sheikh, Egypt. Sotirakou, E., Kladitis, G., Diamantis, N. and Grigoropoulou, H. (1999). "Ammonia and Phosphoures removal in municipal waste water treatment plant with extended aeration" Global Nest:the Int J ,Vol.1,No.1 , 47-53. Su, J.L. and Ouyang, C.F. (1996). Nutrient removal using acombined process with activated sludge and fixed biofilm. Wat.Sci. Tech, Vol.34, No.1-2, 477-486. USEnvironmental Protection Agency (2003). (ACTIVATED SLUDGE)State Acceptance List USA, Office of water, Washington.
Comparison Between Continuous and Batch Flow Activated Sludge Reactor to Remove Nitrate and Phosphate From Domestic Wastewater Waleed M. Sh. Alabdraba, Afaf J. Obed, Masuod M. Hazaa, Safa Badeaa and Manolea Aiden
Abstract In this paper a comparison between continuous and batch flow activated sludge reactor to remove nitrate and phosphate from domestic wastewater, tow bench scale units was operated one work as continuous reactor and the second as batch reactor, the raw wastewater brought up from one of the lifting pump stations in Tikrit city and pass it throw metal screen to prevent floating materials from entering the units. The results shows the batch flow reactor followed by mixing without aeration is the best in bring down total dissolved solids , electrical conductivity and salinity while the best removal of nitrate 63.5% and chemical oxygen demand 91.85% achieved in batch flow reactor. The best removal of phosphate is 96% achieved in batch flow reactor with mixing only before the aeration. the batch flow reactor and the batch flow reactor followed by mixing give the best settling characteristic of sludge, while the pH don’t affected by the flow regime. Key Words:-Nitrate Removal, Phosphate Removal, Batch Flow, Continuous Flow
42
Journal of Environmental Studies [JES] 2012. 9: 43- 51
Original Paper
Modeling of the heating transfer in the karst aquifers for Val d'Orléans city (France) Ali Salim Joodi Department of Environmental Eng., Collage of Engineering, Al-Mustansiriya Univ, Baghdad (Iraq) Rec. 17 Nov, 2011 Accpt. 12 Dec, 2011
Abstract: In karst aquifers, temperature distribution play an additional important role since they carry information about internal aquifer structures. The aim of the present work is to develop a two dimensional heat transfer model in a karst aquifer. Navier Stokes equation is used to simulate the groundwater velocity in the conduit system where the porosity tends to one, and means water velocity was taken into account in the fractured rock. Heat transport equation was applied to simulate the temperature distribution in a karst aquifer, and k- turbulent model is used to simulate the turbulent viscosity. The model was applied to the karst system of Val d'Orléans. Temperatures are measured in thirteen wells with different depth in 29 Jun 2011. Results have shown that the model was not sensitive to the variation of water density, but it is sensitive to the variation of specific heat and density of the rock especially in the fractured system. Also, the model was varied sharply with the velocity of water in sinkhole points, and any variation in the depth of saturated zone. The comparison between measured and calculated temperatures in wells is very good. Key word: Karst aquifers, Heat transport, Conduit and diffuse flow systems, Numerical model and Val d'Orléans highly vulnerable compared to other Introduction: Karst forms when groundwater dissolves groundwater systems, since potential pockets of limestone, dolomite, or gypsum in contaminants can easily reach the groundwater bedrock. This dissolution process increases the (Genthon et al., 2005; O’Driscoll and bulk permeability of the massif, developing a DeWalle, 2006; Dogwiler et al., 2007). conduit network of high hydraulic The use of heat as a groundwater tracer, in conductivity, with short water residence time, contrast to the use of chemical tracers, is and preserving micro fractured blocks with attractive because of the ease of measuring long water-residence time (Dogwiler et al., temperature with high precision (errors as low 2007). Thus, karstification provokes flow as ±0.03 _C). Groundwater temperatures are heterogeneity, increasing the permeability influenced by the temperature of recharge, contrast between conduit flow and diffuse mixing of different waters resulting from flow systems. Karst system is mainly groundwater flow. (Andrieux, 1978; Crowther characterized by four elements. The first is and Pitty, 1982; Roy and Benderitter, 1986; sinkholes which recharge the karst system. Lastennet, 1994; Martin and Dean, 1999; Birk The second is the underground drainages or et al., 2004). have used water temperature conduits which are largely influenced by jointly with other natural hydro dynamical and sinkholes and consequently the water flow in hydro chemical responses, as additional these regions is high. The third is fractured information to characterize the different flow system (diffused system) which is weakly types and the structural influenced by sinkhole and consequently the organization of drainage patterns in karst water flow in these regions is slow. The last is aquifers. Groundwater applications have been spring point in which the water is emerged at developed to model quick-flow in karst the surface. In this context, karst systems are conduits, diffuse flow in fractured and, and the * Corresponding author: Dr. Ali Salim Joodi
[email protected]
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Journal of Environmental Studies [JES] 2012. 9: 43- 51
interaction of these two flow regimes. Fluid flow and solute/ heat-transfer numerical models that include both of these flow regimes include (Benderitter et al., 1993; Liedl and Sauter, 2000; Birk, 2000; Andre and Rajaram, 2005; Birk et al., 2004). With these distributed-parameter models, velocities are estimated from the flow simulation and then are used in the transport simulation. Additional insight into general heat-transfer theory for pipe and channel flow is described by (Gnielinski, 1976; Aravinth, 2000; Beek et al., 1999; Benim et al., 2004). As the conduits are highly influenced by the contamination of rivers (as the water of sinkholes), any information on conduit locations usually is unavailable. For cases where wells or springs have a temperature response that is influenced by conduit flow, the conduit network is globally defined. This paper presents a twodimensional numerical water flow /heat transport model that is explored as an alternative that might be useful to locate the conduit networks in the karst system of the Val d'Orléans. This model simulates the temperature response to recharge in wells and assumes that wells receive at least some of its water from a nearby conduit. The water flow will be simulated in conduit system by Navier Stokes equation, but the model does not simulate the water flow in the fractured system (in which the permeability is less than that in the conduit system). The water velocity in the fractured system will be carried out as mean velocity. The results of the model will be verified with temperatures observed in the wells. The viscosity gradient will be calculated by using K epsilon turbulent model. Characteristics of the experimental field area: The karst aquifer of the Val d’Orléans is the largest in France in terms of flow rate (10 m3/s) and provides the mean water resource of the Orléans city (Albéric and Lepiller, 1998). The Val d’Orléans is considered as a vast depression of the major bed of the Loire river, 37 km long and from 4 to 7 km wide (Fig. 1). The karst aquifer is hosted within an Oligocene carbonate lacustrine deposit occurring in the center of the Paris basin and
called the limestone of Beauce (Guillocheau et al., 2000). This latter formation display variable repartition with a significant primary porosity except for micritic facies, this porosity is increased by karstification leading to a relative high permeability (5E-10 to 2E-9 m2) at hectometric scale (Martin and Noyer, 2003). The latter is overlapped by the quaternary alluvia of the Loire river. The Loire river feeds more than 85% of the water hosted in the carbonated karstic aquifer. The estimated inflow of the Loire river in the sinkhole infiltration area of Jargeau varies from 15 to 20 m3/s and it can reach 100 m3/s during floods (Zunino, 1979; Chéry, 1983; Lepiller and Mondain, 1986). Karst networks are well known in the left bank of the Loire river. The water runs from Jargeau through the karst conduits networks towards the direction of the springs of the Loiret river, (Zunino, 1979; Chéry, 1983; Lepiller and Mondain, 1986), as shown in figure (1). The springs of Loiret river are called the Bouillon and the Abîme, they are considered as the main emergences of the water lost close to Jargeau in the Loire river (from 0.3 to 5 m3/s). The mean aquifer outflow is an underground emergence in the Loire river located around the confluence of Loire - Loiret. Previous studies showed the relation between these springs and the sinkholes points at Jargeau within the Loire river using dye tracer tests (Zunino, 1979; Chéry, 1983; Albéric and Lepiller, 1998; Lepiller, 2001; Albéric, 2008). The main karstic conduits were located according to the depressions of the piezometric surface and to the different connections identified by the tracer tests presented in figure (1).
Figure (1): Underground waters karstic circulations of the Val d’Orléans city (Albéric and Lepiller, 1998).
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Journal of Environmental Studies [JES] 2012. 9: 43- 51
Governing equations: Numerical simulations of fluid flow and heat transport in a karst aquifer were used to investigate the temperature distribution in the karst and by consequence to determine the karstification degree of the karst aquifer. In the present work, Navier Stokes equation is applied to simulate the water velocity in conduit system, as a result to the grand porosity in this system. A uniform velocity is taken in the fractured rock system where the porosity is highly less than that in conduit system. To determine the temperature distribution in the karst, heat transport equation is used. Due o the variation of the temperature in the karst system, the viscosity will be changed, and to calculate this variation K epsilon turbulent model is used. Navier Stokes equation for two dimension is: w
q w q w w q w p 2q w w g t
(1) Heat transport equation in the karst for two dimension is: (1 )r Cr T w Cw T q ww CwT 2T t (2)
K epsilon turbulent model for two dimension is: w
w
k q w w k 2 k G w E t k
(3)
q w w 2 t
(4)
2 C1 G C2 w k k
To calculate the turbulent viscosity, the following equation is used: t C w
k2
…………(5)
Where:
w
is the water density, qw is water velocity vector, t is the time, p is the water pressure, g
is the acceleration gravity, is the porosity of the karst system, r is the rock density, C r is the specific heat of the rock, C w is the specific heat of the water, T is the water temperature, is the heat conductivity, k is the turbulence kinetic energy, is the dissipation rate of
turbulent kinetic energy, G is the production
of turbulence kinetic energy, k , , C1 , C 2 , C
are constants. Les valeurs des constantes sont (Leschziner et Rodi, 1983).
C 0.09 , C1=1.44, C2=1.92, =1.3, k =1 In the present work, the variation in the density of water and rock can be calculated from equations (6) and (7), respectively. The variation in the specific heat of water and rock can be calculated from equation (8) and (9), respectively (Somerton, 1992; Douglas and Jacob, 2004). w (T ) 1043.196 - 42.966623exp (0.006895T) (6) r (T )
2650 1 (T 20) 0.5 10 4
1 C w (T ) 0.0002374 8.06817 108 T 8.03671 1010 T 2
Cr (T ) 1234.257 - 454.546exp (-0.0039733T)
(7) ..(8) (9)
Heat transport in the karst system of the Val d'Orléans: Karst system of the Val d'Orléans has many sinkhole points which are located on the Loire river at the city of Jargeau, and it has many spring points as shown in figure (1). In this work, the temperature is monitored at thirteen wells and one spring point located in the karst system of the Val d'Orléans. In general, water in the conduit includes sinking river water and diffuse flow (from fractured system) entering the conduit along its length. In addition to water from the conduit, a well or spring also might receive local diffuse flow that has not interacted with the conduit. For example, a well that is south of the conduit may induce flow from the conduit and also from diffuse flow within the well’s zone of influence on the north, south, and east sides of the well (Fig. 2) and consequently it can be observed a variation in the water temperature of the well. But in the most cases, it can be observed many wells in which the temperature is constant. This can be attributed to the location of the well, the variation of the water temperature in the well decrease when the well far away from the conduit and vice ve
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Journal of Environmental Studies [JES] 2012. 9: 43- 51
21000 m Sinkhole point Spring source Fractured system
4000 m
Conduit system Well
Figure (2): Schematic diagram of a karst system
Figure (4): Water temperatures measurements in wells of Ligne, Piezometre, Moret 2, and Moret Well of Boires 1 Well of Boires 1
Well of Ligerienne Well of Ligerienne 21
23
20
22 21 20
18
Temperature (C)
Temperature (C)
19
17 16 15 14 13 12 13
18
S
14 13 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28
Depth (m) Well of 2 2 Well ofBoires Boires
Well of Ormeaux 21
22
20
21
19
19
18
Temperature (C)
20 18 17 16 15 14 13 12 7
8
9
10
11
12
13
14
15
16
17
18
19
17 16 15 14 13 12 8
20
10
12
14
Depth (m)
16
18
20
22
24
26
28
Depth (m)
Figure (5): Water temperatures measurements in wells of Ligerienne, Boires 1, Ormeaux, and Boires 2. Well of of Berruet 1 Well Berruet 1
Berruet 3 WellWell of ofBerruet 3 22 20
Le Berruet 4
Temperature (C)
Temperature (C)
16 14
Le Berruet 3 Le Berruet 1 Le Berruet 6
Well location
8
10
12
14
16
18
20
22
24
26
28
17 16 15 14 13 8 10 12 14 16 18 20 22 24 26 28 30 32 34 36 38 40 42 44
30
Depth (m)
Well of 4 Well ofBerruet Berruet 4
Well of Berruet 6
Well of Berruet 6
22
22
21
21
20
20
19 18 17 16 15 14
19 18 17 16 15 14 13 12
12 7
9
11
13
15
17
Depth (m)
19
21
23
25
6
27
8
10
12
14
16
18
20
22
24
Depth (m)
Figure (3): Wells location in the karst system of the Val d'Orléans
Berruet 7 7 WellWell ofofBerruet
o
22 21
Temperature (C)
In these wells, the variation reaches to 12 C, this means that these wells are close to the conduit system. But the temperature is stable in wells of Ligerienne and Ormeaux. Figure (6) shows the wells of Berruet 1 and Berruet 3 are affected by the conduit system but less than that in wells of Boires 1 and Boires 2.
18
Depth (m)
13
Le Berruet 7
19
12
6
Temperature (C)
Le Moret
18
12
Temperature (C)
la Piézométrie
Width (m)
Les Boires 2 Les Ormeaux Les Boires 1 La Ligérienne
La Ligne
E
15
21
Le Moret 2
W
16
Well of Ormeaux
20
Bouillon spring
17
23
22
Loire river
N
18
Depth (m)
Length (m)
Loiret river
19
12 8
Temperature (C)
Depending on the previous description, the temperature is monitored at thirteen wells and one spring point located in the karst system of the Val d'Orléans. Position of wells in the calculational region is illustrated in Fig. (3). The temperature measurements in wells are shown in figures (4,5 and 6). These measurements are provided in 29/06/2011 when the temperature of Loire river and the Bouillon spring were 26.5 oC and 15.6 oC, respectively. figure (4) shows that the water temperature in wells of Ligne, Piezometre, and Moret is nearly stable but in the well of Moret 2, the temperature deceases 3 oC starting from the depth of 12 m. This variation in the temperature can be attributed to the water coming from the conduit system. The variation of groundwater temperature in wells of Boires 1 and Boires 2 is greater than that in the well of Moret 2, as shown in figure (5).
20 19 18 17 16 15 14 13 12 7
9
11
13
15
17
19
21
23
Depth (m)
Figure (6): Water temperatures measurements in wells of Berruet 1, Berruet 3, Berruet 4, Berruet 6, and Berruet 7
46
Journal of Environmental Studies [JES] 2012. 9: 43- 51
and 9). The initial values of water viscosity, kinetic energy and dissipation rate of turbulent kinetic energy are obtained by the following equations: … (10) 0.077U* h … (11) Sgq w
21000 m
470 m
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1
Sinkhole points
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.8
Bouillon spring
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.10.10.10.10.10.10.10.10.10.80.10.80.80.1
Sinkhole points
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.10.10.10.10.10.10.10.10.10.80.10.80.10.10.1
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.80.10.10.10.10.10.10.80.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.80.10.10.10.80.10.10.10.80.80.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.80.10.10.10.10.10.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.80.10.10.10.10.10.10.10.10.80.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.10.10.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1
4000 m
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.10.10.10.10.10.10.10.10.80.80.80.80.80.80.10.10.10.1
Where: h is the mean water depth (depth of saturated zone in the karst aquifer), S is the piezometric of the water slope, U* is the friction velocity which is equal to ghS . The piezometric of the water slope is calculated in each region in the study area according to the piezometric map provided by (Zunino, 1979). Equation (5) is used to calculate the initial value of turbulent kinetic energy. Boundary conditions of the study area are illustrated in fig (8). The finite differences technique is used to solve partial differential equations in the present numerical model. The length and width increments are 5 m. Also, the final time of the model is three months and the time step is 5 min, and the thermal conductivity is 1.3 J/sec.m. oC. u ,v,T ,K ,E 0 y
0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.80.80.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1 0.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.10.1
Figure (7): Porosity field and conduit system pathway suggested in the karst system of the Val d'Orléans (Lepiller, 2001; Albéric, 2008).
Loiret river
u, v, T, K, E 0 x W
P
P
h2
N
Initial conditions constitute values of velocity, temperatures, density and specific heat of the water and rock, water viscosity, turbulent kinetic energy and dissipation rate of turbulent kinetic energy. Concerning the velocity, it is carried out the velocity value measured during the summer season. Then the water velocity inlet to the conduit system is 75 m/hr, this velocity is varied in the conduit system according to Navier Stokes equation, but it is constant in the fractured rock matrix. The velocity inlet to the fractured rock system is a half of previous velocity. Initially the temperature in the study area is that measured in the Bouillon spring on 29 Jun 2011, it was 15.6 oC, expect on the sinkhole points on the Loire river in which the initial water temperature is that measured on Loire river, it was 26.5 oC on 292011. The initial values for the density and specific heat of the water and rock are calculated from equations (6, 7, 8,
Loire river
E
h1 h2 s L
L
S
h1
P: Sinkhole points on Loire river S: Water slope h: Water level
P
Initial values
Mathematical modeling: The study area in the karst aquifer of the Val d'Orléans starts from Jargeau (where the sinkholes on the Loire river are existed) to the last spring point on the Loiret river. The study area is considered as a rectangular area with the length 21000 m and the width 4000m. Two dimension numerical model is carried out to simulate the water temperature distribution in the karst system of the Val d'Orléans. The porosity in conduit system and in the fracture rock system is 90% and 10% respectively. The pathway of the conduit system suggested in the present research is shown in figure (7). This pathway is suggested according to (Lepiller, 2001; Albéric, 2008).
u ,v,T ,K ,E 0 y
Figure (8): Boundary conditions of the two dimension numerical model
Results and discussions: Many parameters influence on the water temperature distribution in a karst aquifer, as the depth of saturated zone, water velocity, viscosity and density effects, porosity, density and specific heat of the rock. Therefore, it was important to study the effect of the variations of these parameters separately to describe the rate and pattern of heat transport and prioritize their influences. Neglecting the density difference between the temperature of Loire river and groundwater temperature is carried out to study the effect of density on the temperature distribution, and keeping a constant density 47
Journal of Environmental Studies [JES] 2012. 9: 43- 51
during a time period of study equal to initial groundwater density. A comparison between isotherms with and without density effect is shown in fig (9). It can be clearly observed, all isotherms are not influenced by the change of water density. This due to the small temperature difference between Loire river temperature (26.5 oC) and groundwater temperature (15.6 oC). To investigate the effect of the variation of water slope along the study reach which is coming from the piezometric map, a constant water slope along the study reach is taken into account. From fig (10), it can be observed that the water slope parameter influences on the behavior of temperature distribution. When the water slope is varied, the distribution of temperature levels advances more in transverse direction as that when the water slope is constant. Length (m)
a
18000
20000
16000
14000
12000
10000
8000
6000
4000
2000
0
500 1000
2000 2500 3000
°C Width (m)
1500
3500 4000
Length (m)
b
18000
20000
16000
14000
12000
10000
8000
6000
4000
2000
0
500 1000
Width (m)
1500 2000 2500 3000 3500 4000
a) When the water density is varied as a function of temperature b) When the water density is constant along the study reach
Figure (9): Effect of water density on the behavior of groundwater temperature distribution.
The water velocity in sinkhole points on Loire river has a great effect on the behavior of temperature distribution along the study reach. As shown in fig (11), all isotherms are advanced longitudinally and transversely with any increase in the water velocity values. This phenomenon can be attributed to the effect of advective term in the heat transport equation, which is responsible for the advance of isotherm along the study reach. Fig (12) shows the effect of water depth in the saturated zone. According to Albéric and Lepiller (1998). the mean depth of saturated zone for the karst system of the Val d'Orléans is 25 m. Any decrease in the depth of saturated zone causes a retardation of the temperature isotherms along the study reach, as shown in fig (12). This can be attributed to the effect of the depth of saturated zone on the friction velocity and water viscosity and by consequence on the temperature distribution. In order to show the effect of the variation of the specific heat and the density of the rock on the behavior of the temperature distribution, equations (7) and (9) are neglected. This means that the specific heat and the density of the rock are constant in the calculations. In the case of the specific heat and the density of the rock are constant, all isotherms are retarded in the transverse direction, but they are advanced in the longitudinal direction, as shown in fig (13). This may be due to the effect of the specific heat and the density of the rock on the domain of fractured system in the karst aquifers only.
Length (m)
a
20000
18000
16000
14000
12000
10000
Length (m) 8000
6000
4000
2000
a
0
20000
18000
16000
14000
12000
10000
8000
6000
4000
2000
0
500
500
1000
2500 3000
b
1500 2000 2500 3000
3500
3500
4000
4000
Length (m) 20000
18000
16000
14000
12000
10000
8000
6000
4000
2000
1000
b
0
°C Width (m)
2000
°C Width (m)
1500
Length (m) 20000
18000
16000
14000
12000
10000
8000
6000
4000
2000
0
500
500
1000
1500
2000
2000
2500
2500
3000
Width (m)
1500
Width (m)
1000
3500
3000
4000
3500 4000
a) When the water slope is varied along the study reach b) When the water slope is constant along the study reach
Figure (10): Effect of water slope on the behavior of groundwater temperature distribution.
a) When the water velocity is 75 m/hr b) When the water velocity is 144 m/hr
Figure (11): Effect of water velocity on the behavior of groundwater temperature distribution.
48
Journal of Environmental Studies [JES] 2012. 9: 43- 51
Length (m)
a
20000
18000
16000
14000
12000
10000
8000
6000
4000
2000
0
500 1000
°C Width (m)
1500 2000 2500 3000 3500 4000
Length (m)
b
20000
18000
16000
14000
12000
10000
8000
6000
4000
2000
0
500 500 1000 1000
Width (m)
1500 1500 2000 2000 2500 2500 3000 3000 3500 3500 4000 4000
a) When the depth of saturated zone is 25 m b) When the depth of saturated zone is 5 m
Figure (12): Effect of the depth of saturated zone on the behavior of groundwater temperature distribution. Length (m)
a
20000
18000
16000
14000
12000
10000
8000
6000
4000
2000
0
500 1000
2000 2500 3000
°C Width (m)
1500
3500 4000
Length (m)
b
20000
18000
16000
14000
12000
10000
8000
6000
4000
Measured Calculated % temperatur temperatur Erro e e r 15.1 15.7 3.9 Berruet 1 16.2 16 1.2 Berruet 3 13.3 15.1 13.5 Berruet 4 17.3 16 7.5 Berruet 6 17.6 17.8 1.1 Moret 22.1 20.1 9 Boires 1 14.4 15.1 4.8 Ligne 12.9 15.2 17.8 Piezometri 17.3 17.1 1.1 Moret 2 eBoires 2 18.8 18.5 1.5 20.5 20.5 0 Ligerienne Bouillon 15.6 15.1 3.2 spring (1): Comparison between measured and Table calculated temperatures in wells. Well
2000
0
500 1000
2000 2500
Width (m)
1500
3000 3500 4000
a) When the density and specific heat of the rock is varied b) When the density and specific heat of the rock is constant (density= 2649.13 kg/m3, specific heat= 825.1 J/kg.k)
Figure (13): Effect of the density and specific heat of the rock on the behavior of groundwater temperature distribution
In order to verify the accuracy of the present numerical model, a comparison between measured and calculated temperatures in wells is occurred. The best results are obtained when the water velocity in sinkhole points is 80 m/hr, the porosity is 10% in the fractured system and 80% in the conduit system and the depth of saturated zone is 25 m. Table (1) displays this comparison with the percentage error for each well. It can be clearly observed that the results of the model are very good compared with the measured temperature. The percentage error of the model ranges from zero to 17.8 percent.
Conclusions In karst aquifers, temperature signals play an additional important role since they carry information about internal aquifer structures. A two dimension heat transport numerical model was developed to simulate the temperature distribution in a karst aquifers composed conduits and fractured systems. The model was based on the Navier Stokes equation to simulate the groundwater velocity in the conduit system where the porosity tends to one, heat transport equation to simulate the temperature distribution in a karst aquifer, and finally k- turbulent model to simulate the turbulent viscosity. The model was applied to the karst system of the Val d'Orléans. This system is very developed in which there are many sinkhole points on the Loire river and many spring point along the Loiret river. Temperatures are measured in thirteen wells with different depth in 29 Jun2011 when the temperature of Loire river and the Bouillon spring were 26.5 oC and 15.6 oC. Calculated results have shown that the model is not sensitive to the variation of water density, but it is sensitive to the variation of specific heat and density of the rock especially in the fractured system. Also, the model is very sensitive to any variation on the water velocity in sinkhole points, and any variation in the depth of saturated zone. The influence of the variation of the groundwater slope along the study reach is small compared 49
Journal of Environmental Studies [JES] 2012. 9: 43- 51
with other parameters. The best results are occured when the water velocity in sinkhole points is 80 m/hr, the porosity is 10% in the fractured system and 80% in the conduit system and the depth of saturated zone is 25 m. Finally, it was observed that the comparison between measured and calculated temperatures in wells is very good. References Albéric, P. and Lepiller, M. (1998). Oxydation de la matière organique dans un système hydrologique karstique alimenté les pertes fluviales (Loiret, France). Water Resources 32, 2051– 2064 Albéric, P. (2008). Les trios pertesémergences (ou inversacs) du domaine de la source (Loiret). Colloque national d’Hydrogéologie. May 16 and 17, Orléans –France Andre, B.J., Rajaram, H. (2005). Dissolution of limestone fractures by cooling waters: Early development of hypogene karst systems. Water Resources Research 41 (1), 1–16. Andrieux, C. (1978). The experiences form the temperature in the karst (in French). Colloque de Tarbes, Le karst: son originalité physique, son importance économique. Association des Géologues du SudOuest (AGSO), Orleans, France, 48–63 Aravinth, S. (2000). Prediction of heat and mass transfer for full developed turbulent fluid flow through tubes. International Journal of Heat and Mass Transfer 43, 1399–1408. Beek, W.J., Muttzall, M.K., van Heuven, J.W. (1999). Transport Phenomena, second edition. John Wiley & Sons Ltd., West Sussex, England. 329 p. Benderitter, Y., Roy, B., Tabbagh, A. (1993). Flow characterization through heat transfer evidence in a carbonate fractured medium: first approach. Water Resources Research 29 (11), 3741–3747. Benim, A.C., Cagan, M., Gunes, D. (2004). Computation analysis of transient heat transfer in turbulent pipe flow.
International Journal of Thermal Sciences 43, 725–732. Birk, S. (2002). Characterization of Karst Systems by Simulating Aquifer Genesis and Spring Responses: Model Development and Application to Gypsum Karst. Tübinger Geowissenschaftliche Arbeiten, vol. 60. Reihe C. Institut und Museum für Geologie und Paläontologie der Universität Tübingen, Tübingen, Germany. . Birk, S., Liedl, R., Sauter, M. )2004(. Identification of localized recharge and conduit flow by combined analysis of hydraulic and physico– chemical spring responses (Urenbrunnen, SW-Germany). Journal of Hydrology 286: 179–193 Chery, J.L. (1983). Etude hydro chimique d’un aquifère karstique alimenté par perte de cours d’eau (la Loire). Thèse 3e cycle, Orléans Crowther, J., Pitty, A.F. (1982). Water temperature variability as an indicator of shallow-depth groundwater behaviour in limestone areas in west Malaysia. Ournal of Hydrology 57, 137–146 Dogwiler, T., Wicks, C.M., Jenzen, E. (2007). An assessment of the applicability of the heat pulse method toward the determination of infiltration rates in karst losing stream reaches. Journal of Cave and Karst Studies 69 (2), 237– 242. Genthon, P., Bataille, A., Fromant, A., D’Hulst, D., Bourges, F. (2005). Temperature as a marker for karstic waters hydrodynamics. Inferences from 1 year recording at la Peyrere cave (Ariege, France). Journal of Hydrology 311 (1–4), 157–171. Gnielinski, V. (1976). New equations for heat and mass transfer in turbulent pipe and channel flow. International Chemical Engineering 16 (2), 359– 368.
50
Journal of Environmental Studies [JES] 2012. 9: 43- 51
Guillocheau, F., Robin, C., Allemand, P., Bourquin, S., Brault, N., Dromart, G., Friedenberg, R., Garcia, J., Gaulier, J., Gaumet, F., Grosdoy, B., Hanot, F., Le Strat, P., Mettraux, M., Nalpas, T., Prijac, C., Rigollet, C., Serrano, O., Grandjean, G. (2000). Meso-Cenozoic geodynamic evolution of the Paris Basin: 3D stratigraphic constraints Geodin. Acta 133(4), 189– 246 Lastennet, R. (1994). Role of unsaturated zone in the functioning of karst aquifers: approach for the physico–chemical and isotopic study of input and output (springs) of Ventoux massif (Vaucluse) (in French). PhD Thesis, Univ. Avignon and Pays de Vaucluse, France, 239 pp Lepiller, M. (2001). Traçages appliqués à la dynamique des aquifères karstiques. Géologue (129), 79–84 Lepiller, M. and Mondain, P.H. (1986). Les traçages artificiels en hydrogéologie karstique. Hydrogéol 1, 33–52 Liedl, R., Sauter, M. (2000). Characterization of karst groundwater processes, using models of aquifer genesis and heat transport. Grundwasser 5 (1), 9–16. Martin, J.B., Dean, R.W. (1999). Temperature as a natural tracer of short residence
times for groundwater in karst aquifers. In: Palmer AN, Palmer MV, Sasowsky ID (eds) Karst Modeling. Spec. Publ. 5, Karst Waters Institute, Leesburg, VA, 236–242 Martin, J.C. and Noyer, M.L. (2003). Caractérisation du risque d’inondation par remontée de nappe sur le Val d’Orléans. Etude hydrogéologie, BRGM O’Driscoll, M.A., DeWalle, D.R (2006). Stream–air temperature relations to classify stream–ground water interactions in a karst setting, central Pennsylvania, USA. Journal of Hydrology 329 (1–2), 140–153. Roy, B., Benderitter, Y. (1986). Natural thermal transfer in a superficial fissured carbonate system (in French). Bull Soc Géol France 2 (4), 661–666 Yakhot, V., Orszag, S.A., Thangam, S., Gatski, T.B. and Speziale, G.C. (1992). Developments of Turbulence Models for Shear Flows by a Double Expansion Technique, Physics of Fluids A, 4 (7), 1510–1520 Zunino, (1979). Contribution à l’étude hydrogéologique du Val d’Orléans. Ph.D. thesis, Orleans University
الملخص العزبى
)نمذجت نقل الحزارة في طبقت المياه الجوفيت الكارستيت لمدينت اورليانز (فزنسا :الخالصت ْذف ْزا انؼًم. دسخخ انحشاسح رهؼت دٔس يٓى خصٕصب نًؼشفخ يؼهٕيبد حٕل رشكيت ْزِ األٔسبط،في األٔسبط انكبسسزيخ اسزخذيذ نحسبة انسشع فيNavier Stokes يؼبدنخ.ْٕ رطٕيش ًَٕرج سيبضي ثُبئي األثؼبد االَزشبس انحشاسح في انكبسسذ . ٔرى اخز قيًخ يؼيُخ ٔسطيخ نهسشػخ في انٕسط انًزشقق،)conduit( انٕسط انكبسسزي انزي ركٌٕ فيّ انُفبريخ رًيم نقيًخ ٔاحذ نحسبة انزغيش في قيىk- ٔرى اسزخذاو يٕديم،يؼبدنخ اَزقبل انحشاسح اسزخذيذ إليدبد رٕصيغ دسخبد انحشاسح في انكبسسذ حيث رى قيبط دسخبد انحشاسح،) انًُٕرج انشيبضي رى رطجيقخ في انُظبو انكبسسزي في يذيُخ ٔسنيٌٕ (فشَسب.انهضٔخخ انذايًُيكيخ انُزبئح ثيُذ أٌ انًُٕرج ال يزأثش ثأي رغيش في انكثبفخ ٔنكُّ حسبط ألي رغيش في.29 Jun 2011 في ثالثيٍ ثئش يبئي ثزبسيخ كزنك أٌ انًُٕرج حسبط خذا ألي رغيش في قيًخ انسشع انذاخهخ نهُظبو.كثبفخ انصخٕس انكبسسزيخ خصٕصب في انٕسط انًزشقق إٌ انًقبسَخ ثيٍ قيى دسخبد انحشاسح انًقبسخ ٔانًحسٕثخ ثيُذ أٌ انًُٕرج.انكبسسزي ٔ أي رغيش في قيًخ ػًق انًُطقخ انًشجؼخ .خيذ خذا
51
Journal of Environmental Studies [JES] 2012. 9: 53-63
Original Paper
Characteristics of the Hydraulic Jump in Trapezoidal Channel Section Sadiq Salman Muhsun Environmental Engineering Dept., College of Eng. Al-Mustansiriya University, Baghdad, Iraq. Rec. 17 Nov, 2011 Accpt. 12 Dec, 2011
Abstract In this study, characteristics of the hydraulic jump in trapezoidal channel sections were analyzed and a general equation represents the solution of the hydraulic jump in the channels of arbitrary cross-sections (rectangular, triangular & trapezoidal) was driven depending on the momentum principle. The solution of the models was provided using Newton Raphson method. Consequently, Tables and charts of family curves of the conjugate depths ratio (r=y2/y1) have been prepared, for a very wide range values of Froude numbers and section ratios (k=b/zy). For each type of cross sections, the efficiency of the energy dissipation of the hydraulic jump was also analyzed and compared with each others. The relationship between the initial and sequent Froude numbers (FD1 and FD2) has been indicated for various values of k1=b/zy1. Depending on the results of conjugate depths ratio r = y2 / y1, the length of the hydraulic jump were estimated for a very wide range of k1=b/zy1, using two suggested models. It was found that the channel shape has insignificant effect on the efficiency of the energy dissipation of the hydraulic jump, although the triangular section tends to be more efficient than the others by about 10 percent in higher FD1. When (FD1 > 6), the velocity head after the jump could be neglected. When the section ratio k1 is approximately 3, the length ratio of the hydraulic jump (Lj / y2) reaches to a maximum value independent on the value of FD1. In all cases, it was shown that the comparison of the theoretical results with other experimental data indicate a very good agreement Key words: hydraulic jump - sequent depth ratio - jump in trapezoidal and triangular channels - Conjugate Depth, Energy Dissipaters Introduction The hydraulic jump is a natural phenomenon which may be defined as a sudden and turbulent passage of water from supercritical flow to subcritical state, (Modi, 2004). The abrupt change in flow condition is accompanied by considerable turbulence and energy losses. The hydraulic jump commonly occurs with natural flow conditions and with proper design can be an effective means of dissipating energy at hydraulic structures. Expressions for computing the before and after jump depth ratio (conjugate depths) and the length of jump are needed to design energy dissipaters that induce a hydraulic jump. For this reason, the hydraulic jump is often employed to dissipate energy and control erosion at storm water management structures.
Hydraulic jumps are commonly experienced in rivers, canals, industrial applications and manufacturing processes. (Montes, 1979; Chow, 1994; Treske, 1994; Reinaur and Hager, 1995; Chanson and Montes, 1995; Chanson, 2007 and Murzyn, 2007; studied the undular hydraulic jump, described its characteristics where the values of the Froude number in which the jump is no longer undular was calculated neglecting the effect of the channel width. The jump height, however, may be predicted quite accurately using momentum theory alone Hotchkiss et al., (2003). Typically, the discharge and upstream depth are already known, and what remains to be determined is the downstream “sequent depth”, Chadwick et al., (2004). The purpose of this study, is to develop a general solution of the sequent depth problem in trapezoidal channel section * Corresponding author: Dr. Sadiq Salman
[email protected]
53
Journal of Environmental Studies [JES] 2012. 9: 53-63
(rectangular, triangular & trapezoidal), based on the momentum principle law. Such a solution will be useful to analyze the characteristics flow of a turbulent hydraulic jump and to determine the length of the hydraulic jump as well as the efficiency dissipation. Momentum Principle Because of energy losses, the size and location of the hydraulic jump cannot be predicted using the energy equation. However, because momentum is conserved across hydraulic jumps under the assumptions of this study, momentum theory
could be applied to determine the jump size and location Hotchkiss et al., (2003). Figure 1 indicates the control volume used and the forces involved. Distribution of pressure in the upstream and downstream sections is assumed to be hydrostatic. So, applying the momentum equation in a frictionless channel considering the above assumptions, leads the momentum equation in the term of the specific force to be: Q2 Q2 + Z C 1 A1 = + Z C 2 A2 = F gA 1 gA 2
F1 = F
Or
(1) (2)
2
2
V1 /2g
jump
E2
E1
2
V2 /2g y2
y1
Fig.1: Hydraulic jump control volume .
Where: F: Specific force Q: Flow rate g: Gravity acceleration A1 & A2: Cross-sectional area before and after the jump, respectively. ZC1 & ZC2: Distances of the centroids sections from the free surface area before and after the jump, respectively. Consider that:
A = by + zy
T = b + 2 zy F
r
=
V gy
F
D
=
V gD
2
(3) (4) (5) (6)
Where: T: Top width of the sectional area. b: Bottom width of the sectional area. z: side slope V: Mean velocity. Fr: Froude number in term of the depth of flow y. FD: Froude number in term of the hydraulic depth D = A/T.
Now, define a dimensionless factor k to be a section ratio such that:
k=
b
(7)
z y
Consequently, Eqs. (3 & 4) could be rewritten as: (8) A = zy 2 ( k + 1)
T = zy(k + 2)
(9)
Also, it could be seen that: k+2 Fr k +1
FD =
(10)
According to the section ratio k, the shape of the channel section will take the following form: when k = 0, the section is a triangular shape. and, when k = ∞, the section is a rectangular shape. While for 0 < k < ∞, the section is a trapezoidal shape. By taking the moments about the top axis of a trapezoidal channel section, the centroid Position Zc, could be determined as:
Z
C
=
1 1 k + 2 3 k + 1
y
(11)
54
Journal of Environmental Studies [JES] 2012. 9: 53-63
Substituting the values of various terms of Eq. 2, considering Eqs. (7 to 11) and simplifying, the specific force before the jump F1 will take the following form: 1 4 2 F (k + 3 k + 2 ) + k + k + (12) 2
F1 = Z y 1
2
2
r
3
2 (k + 2 )
3 1
3
By the same way, it could be seen that: Fr 3 F2 = Z y 2
2
(k
2
1 + 3k + 2 + k 2 (k + 2 )
)
2
4 2 + k + 3 3 2
(13)
Where the subscripts 1 & 2, refer to the corresponding variable of section 1 and 2 respectively. It is necessary now to represent the variables of Eq.13 in term of the same variables of the section 1, considering that:
k2 =
b = r −1 k 1 zy 2
(14)
Where: r: Conjugate depths ratio of the initial and sequent depths, (y2 / y1) . Also, it could be seen that: A1
2
A2
2
Fr
= r
2
= r
2
or F r
2
2
k1 + 1 k1 + r
−2
−1
A1
2
A2
2
(15)
2
Fr
k +1 = r − 3 1 k1 + r
2
(16 a)
1
2
Fr
2
(16 b)
1
So, Eq.13 will take the following form: −2 r Fr 3 F2 = Z y 2
2
k +1 k+r
2
(r
−2
k
2
1 + 3 r −1 k + 2 + r −1 k 2 (k + 2 r )
Satisfy the condition of Eq.2, taking in the count Eqs. (10, 12, & 17), the following
)
2
+
4 2 k + r 3 3 1
equation is produced after some tedious mathematical steps:
3 2 5k 3 3k 2 (k +1) 2 (k +1) 2 k (k +1) r −3FD r + +1 r + +1 (k +1) r + +k −3FD =0 2 (k +2) (k +2) 2 2 4
Equation 18 represents the relationship of the Conjugate depths ratio of a hydraulic jump in a horizontal trapezoidal channel. This equation could be simplified by considering that: 5k B = + 1 2
(19 a)
3k C = + 1 (k + 1) 2
(20 a)
k2 2 ( k + 1) (k + 1) D = + k − 3FD 2 (k + 2)
E = −3FD
2
( k + 1) 3 (k + 2)
(21 a)
(22 a)
Where k is k1 and FD is FD1. So, Eq. 18 will reduce to the following form:
r4 + B r3 +C r2 + D r + E = 0
(23 a)
(17)
(18)
Conjugate Depths - Initial and Sequent Depths: For a given values of FD1 and k1, the solution of Eqs. (18 or 23a) represents the conjugate depths ratio r = y2/y1. As it is known, this Equation has four roots. The signs of the second and the third term of Eq.23a (B & C) are always positive, while the fifth term E, is always negative. The forth term D, may have a positive or a negative sign depending on the values of FD1 and k1. According to Decard theory, equation 23 has always a unique positive root whatever the sign of the term D, and that is the required solution, (Hoffman, 2001). The researcher found that Newton–Raphson method is a very good technique to provide the results. Also, fixed-point method may be a useful alternative technique to determine the mathematical solution for the depths upstream and downstream of the hydraulic jump, (Vatankhah, 2008). Fig.2 represents a dimensionless chart for the conjugate depths 55
Journal of Environmental Studies [JES] 2012. 201 9: 53-63
yi 2 = 0 . 5 1 + 8 F rj yj
− 1
(
A = B = 1 + 2. 5 k 2 + 1. 5 k 2
2
2
)
C = 1 + k 2 − 3k 2η 2 − 3k 2 η 2
(
2
D = − 3η
E = − 3η
k=0 k=0.5 k=1 k=2 k=3 k=4 k=6 k=8 k=10 k=15 k=20 k=30 k=40 k=60 k=100 Rect.
25
20
15
10
5
0 0
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
FD 1=V/(gD)0.5
Fig.2: Family curves for the conjugate depths ratio r, corresponding to the upstream Froude number FD1 and k1.
(24)
In many practical and designed cases the problem is to find the initial depth y1 for a given control depth y2 in the downstream of the jump. In this case the following model (Eq.23 b), will be used to provide the conjugate ratio r,, which depends on the relationship between Eqs. (10 , 14 & 16) and Eq.18. The solution of this model was achieved by trail and error method with helpful of the computer. However, all the results were represented in Fig.3 and Table 2.
(
30
r = y2/y1
ratio r for various upstream Froude numbers FD1, corresponding to a very wide range of a section ratio k1, from zero (i.e., triangular shape) to infinity (i.e., rectangular shape). As it is shown, the conjugate depths ratio has a little significant change at high section ratios for the same Froude numbers. ers. Also, for all values of k1, when FD1 < 2, the conjugate depths ratio r is near the corresponding value of the rectangular section. In case of the rectangular section (where k1 = ∞), the curve indicates a completed agreement with the results of the standard ndard form of the hydraulic jump usually used in a rectangular channel section, Eq.24. For more details, notice Table 1.
− 6 k 2η
2
(19 b)
)
(20 b)
)
(21 b)
2
Fig.3: Family curves for the conjugate depths ratio r, corresponding to the Downstream Froude number FD2 and k2.
It could be seen that, when FD2 is more than 0.5 the conjugate depth ratio (r =y2/y 1) has the same value for any section ratio k2 . For this reason the arrangement values of FD2 in Table (2) was concentrated on the low values of FD2. Fig (4) shows the relationship between the upstream Froude number FD1 and the corresponding FD2 for varies values of k1. The Figure indicates that when FD1 is greater than 20, the minimum value of FD2 approaches to 0.1 for the triangular section and 0.15 for the rectangular section. Indicating that the shape of the section has a little effect on the values of FD2 when FD1 is greater than 2 and has insignificant effect when the value of FD1 is less than 2.
(22 b)
1.0 0.9 k1=0
2
k +1 k +1 η = Fr = 2 r5 2 FD22 rk2 +1 k2 + 2
0.8
2 1
(22 C)
k1=5 k1=10
0.7
k1=100 0.6 FD2
2
Rect. k=∞
0.5 0.4 0.3
Therefore,
Eq.
18
will
be:
0.2 0.1
4
3
2
A r + B r +C r + D r + E = 0
0.0
(23 b)
0
2
4
6
8
10
12
14
16
18
20
FD1
Fig.4: Relationship between FD1 and FD2 for varies values of k1.
56
Journal of Environmental Studies [JES] 2012. 9: 53-63
F
k1=0
k1=.5
k1=1
k1=2
k1=3
k1=4
k1=5
k1=6
k1=7
k1=8
k1=9
k1=10
k1=12
k1=15
k1=20
k1=30
k1=40
k1=60
k1= 100
Rect. k=∞
Rect. Eq.24
1.000 1.702 2.284 2.799 3.271 3.710 4.125 4.519 4.897 5.261 5.952 6.606 7.228 7.825 8.399
1.000 1.842 2.545 3.170 3.741 4.275 4.778 5.257 5.716 6.157 6.998 7.792 8.549 9.274 9.972
1.000 1.935 2.726 3.432 4.079 4.684 5.255 5.800 6.321 6.823 7.780 8.683 9.545 10.370 11.165
1.000 2.051 2.963 3.785 4.543 5.254 5.927 6.569 7.186 7.780 8.912 9.983 11.004 11.984 12.928
1.000 2.120 3.112 4.015 4.853 5.641 6.389 7.104 7.791 8.454 9.719 10.917 12.061 13.158 14.216
1.000 2.165 3.215 4.179 5.078 5.926 6.732 7.505 8.248 8.966 10.338 11.639 12.882 14.076 15.227
1.000 2.197 3.290 4.301 5.249 6.145 7.000 7.820 8.610 9.374 10.835 12.222 13.549 14.824 16.054
1.000 2.220 3.348 4.397 5.384 6.321 7.216 8.076 8.905 9.708 11.246 12.708 14.106 15.452 16.750
1.000 2.238 3.393 4.473 5.494 6.464 7.394 8.288 9.152 9.989 11.593 13.120 14.583 15.990 17.350
1.000 2.253 3.430 4.536 5.585 6.585 7.544 8.468 9.362 10.229 11.892 13.477 14.997 16.460 17.874
1.000 2.264 3.460 4.589 5.662 6.687 7.673 8.623 9.543 10.437 12.153 13.790 15.361 16.874 18.338
1.000 2.274 3.485 4.633 5.727 6.775 7.784 8.758 9.702 10.619 12.383 14.068 15.685 17.244 18.752
1.000 2.289 3.525 4.705 5.834 6.920 7.968 8.982 9.967 10.925 12.772 14.539 16.238 17.878 19.466
1.000 2.304 3.568 4.783 5.952 7.081 8.175 9.237 10.271 11.279 13.227 15.095 16.895 18.636 20.325
1.000 2.320 3.614 4.868 6.084 7.264 8.413 9.533 10.627 11.696 13.770 15.768 17.699 19.571 21.391
1.000 2.337 3.663 4.962 6.231 7.473 8.689 9.881 11.051 12.199 14.439 16.610 18.719 20.772 22.775
1.000 2.346 3.689 5.012 6.312 7.589 8.845 10.081 11.297 12.495 14.839 17.122 19.347 21.522 23.649
1.000 2.354 3.716 5.065 6.398 7.715 9.016 10.301 11.572 12.828 15.299 17.718 20.091 22.419 24.705
1.000 2.362 3.738 5.109 6.471 7.823 9.165 10.496 11.817 13.128 15.721 18.276 20.797 23.283 25.738
1.000 2.372 3.772 5.179 6.589 8.000 9.412 10.825 12.238 13.651 16.478 19.305 22.133 24.961 27.789
1.000 2.372 3.772 5.179 6.589 8.000 9.412 10.825 12.238 13.651 16.478 19.305 22.133 24.961 27.789
D1
1 2 3 4 5 6 7 8 9 10 12 14 16 18 20
Table. 1. Conjugate depths ratio of a hydraulic jump in trapezoidal channel sections for a given y1 with varies k1.
F D2
k2 = 0
k2 = 0.05
k2 = 0.075
k2 = 0.1
k2 = 0.15
k2 = 0.2
k2 = 0.25
k2 = 0.3
k2 = 0.35
k2 = 0.4
k2 = 0.45
k2 = 0.5
k2 = 0.55
k2 = 0.6
0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0.55 0.6 0.7 0.8 0.9 1
8.219 5.518 4.176 3.375 2.843 2.466 2.183 1.964 1.789 1.646 1.527 1.340 1.199 1.089 1.000
9.786 6.158 4.511 3.575 2.974 2.555 2.247 2.011 1.824 1.672 1.547 1.351 1.205 1.091 1.000
10.619 6.486 4.679 3.675 3.038 2.599 2.278 2.033 1.841 1.685 1.556 1.356 1.207 1.092 1.000
11.472 6.818 4.848 3.774 3.102 2.642 2.308 2.055 1.857 1.697 1.565 1.361 1.210 1.093 1.000
13.207 7.485 5.184 3.970 3.226 2.726 2.368 2.099 1.889 1.721 1.583 1.371 1.215 1.095 1.000
14.932 8.145 5.514 4.161 3.347 2.808 2.425 2.140 1.919 1.744 1.600 1.381 1.220 1.097 1.000
16.608 8.789 5.835 4.346 3.464 2.886 2.480 2.179 1.948 1.765 1.617 1.390 1.225 1.099 1.000
18.212 9.409 6.144 4.524 3.576 2.961 2.532 2.217 1.976 1.786 1.632 1.398 1.229 1.101 1.000
19.732 10.003 6.441 4.695 3.684 3.033 2.583 2.253 2.002 1.805 1.647 1.407 1.233 1.103 1.000
21.164 10.568 6.725 4.858 3.787 3.102 2.630 2.288 2.028 1.824 1.661 1.414 1.237 1.104 1.000
22.507 11.103 6.994 5.014 3.885 3.167 2.676 2.320 2.052 1.842 1.674 1.422 1.241 1.106 1.000
23.766 11.608 7.250 5.162 3.978 3.230 2.719 2.351 2.074 1.859 1.687 1.429 1.245 1.107 1.000
24.943 12.083 7.492 5.302 4.067 3.289 2.761 2.381 2.096 1.875 1.699 1.435 1.248 1.108 1.000
26.045 12.531 7.721 5.435 4.151 3.346 2.800 2.409 2.117 1.890 1.710 1.442 1.251 1.110 1.000
Table. 2. Conjugate depths ratio of a hydraulic jump in trapezoidal channel sections for a given y2 with varies k2.
57
Journal of Environmental Studies [JES] 2012. 9: 53-63
F D2
k2 = 0.7
k2 = 0.8
k2 = 0.9
k2 = 1
k2 = 1.25
k2 = 1.5
k2 = 1.75
k2 = 2
k2 = 2.5
k2 = 3
k2 = 3.5
k2 = 4
K2 = ∞ Rect.
Eq.24
0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0.55 0.6 0.7 0.8 0.9 1
28.041 13.350 8.142 5.681 4.307 3.450 2.873 2.462 2.155 1.919 1.731 1.453 1.257 1.112 1.000
29.793 14.074 8.518 5.902 4.447 3.545 2.939 2.509 2.190 1.945 1.751 1.464 1.263 1.114 1.000
31.336 14.718 8.854 6.100 4.574 3.630 2.999 2.552 2.222 1.968 1.768 1.474 1.268 1.116 1.000
32.702 15.290 9.154 6.278 4.688 3.707 3.053 2.591 2.250 1.989 1.784 1.483 1.273 1.118 1.000
35.499 16.472 9.778 6.651 4.929 3.870 3.168 2.675 2.312 2.035 1.818 1.502 1.282 1.122 1.000
37.637 17.382 10.264 6.943 5.118 4.000 3.260 2.741 2.361 2.072 1.846 1.517 1.290 1.125 1.000
39.311 18.098 10.648 7.176 5.270 4.104 3.334 2.795 2.401 2.102 1.869 1.530 1.297 1.128 1.000
40.649 18.673 10.958 7.364 5.394 4.190 3.395 2.840 2.434 2.127 1.888 1.540 1.303 1.130 1.000
42.638 19.532 11.423 7.649 5.581 4.319 3.488 2.909 2.485 2.166 1.917 1.557 1.311 1.134 1.000
44.031 20.136 11.751 7.851 5.715 4.413 3.556 2.958 2.523 2.194 1.938 1.569 1.318 1.136 1.000
45.053 20.580 11.994 8.001 5.815 4.482 3.606 2.996 2.551 2.215 1.955 1.579 1.323 1.138 1.000
45.830 20.919 12.179 8.115 5.891 4.536 3.645 3.025 2.573 2.232 1.967 1.586 1.327 1.140 1.000
50.984 23.181 13.431 8.899 6.421 4.906 3.922 3.234 2.732 2.355 2.062 1.642 1.357 1.153 1.000
50.981 23.181 13.431 8.899 6.421 4.912 3.922 3.233 2.732 2.355 2.062 1.642 1.357 1.153 1.000
Table. 2. Continued
Jump Characteristics The characteristics of the hydraulic jump in horizontal trapezoidal channel sections represented by some of terminologies will be discussed below. Energy Dissipation Efficiency Hydraulic jumps have been widely used for energy dissipation in hydraulic constructions. Many researchers have paid their attention to them for a long time, (Hashmi, 2003) & (Chaudhry, 2008). The hydraulic jump naturally dissipates energy through turbulence, which can be highly erosive if proper channel protection is not installed, (Hager, 1992). It is therefore preferable, when a hydraulic jump is expected, to control the size and location of the jump in order to localize energy dissipation and erosion, (Stahl and Hager, 1999). The energy loss due to the hydraulic jump is equal to:
∆E = E1 − E2
(25)
With E
=
y +
V 2 2 g
(26)
Where: ∆E: Energy loss due to the jump. E1: Specific energy before the jump. E2: Specific energy after the jump. The ratio of (E2 / E1), represents the efficiency of the jump, (Ef), so: E Ef = 2 E1
Therefore, the relative losses is equal to:
(27)
E ∆E =1− 2 E1 E1
(28)
The difference between the conjugate depths is the height of the jump hj, and the ratio hj/E1, represents the relative height: hj
y2 y (29) − 1 E1 E1 E1 Where: y1/E1: Relative initial depth. y2/E1: Relative sequent depth. It is important to express all the above ratios in term of dimensionless functions of FD1. Depending on Eq.26 and using Eqs.(6 & 10), the relative initial depth could be expressed as: =
y1 2 (k + 2 ) 2 = = E 1 2 (k + 2 ) + (k + 1) F D 1 2 2 + Fr 1
(30)
So, the relative sequent depth will be: y2 y (31) = 1 r E1 E1 Applying Eq.26 at the downstream of the jump, considering Eqs. (14 to 16), results: E2 (k + 1 )3 2 (32) = r + F D1 2 2 y1 2 r (k + 2 )(k + r ) Consequently, from Eqs. (30 & 32), the efficiency will take the following form: E2 2(k + 2)) (k +1)3 2 = xr + 2 FD1 2 E1 2(k + 2)) + (k +1) FD1 2r (k + 2)(k + r)2
(33)
It should be remembered that, the value of r in the above equations, represents the solution of Eq.23a corresponding to the values of FD1 and k1. Since the efficiency and the other relative's definitions become 58
Journal of Environmental Studies [JES] 2012. 9: 53-63
functions of FD1, plotting them against Froude number produces set of chrematistic
curves for various values of k1, see Fig.5.
1.0
Rectangular channel
0.9
E2/E1
k= ∞
0.8
y2/E1
∆E/E1
0.7 0.6
Ratios of characteristics of the jump
Ratios of characteristics of the jump
1.0
hj/E1 y1/E1
0.5 0.4 0.3 0.2 0.1
Traingular channel k=0
0.9
y2/E1
∆E/E1
0.7
hj/E1 y1/E1
0.6 0.5 0.4 0.3 0.2 0.1 0.0
0.0 1
2
3
4
5
6
7
8
9
1
10
2
3
4
5
6
7
8
9
10
FD1
FD1
1.0 Trapezoidel channel k = 5
0.9
Ratiosof characteristicsof thejump
1.0 Ratios of characteristics of the jump
E2/E1
0.8
E2/E1
0.8
y2/E1
∆E/E1
0.7
hj/E1 y1/E1
0.6 0.5 0.4 0.3 0.2 0.1 0.0
Trapezoidel channel k = 40
0.9
E2/E1
0.8
y2/E1
∆E/E1
0.7
hj/E1
0.6
y1/E1
0.5 0.4 0.3 0.2 0.1 0.0
1
2
3
4
5
6
7
8
9
10
1
2
3
FD1
4
5
6
7
8
9
10
FD1
Fig.5: Characteristic curves of the jump in trapezoidal channel sections for varies k1.
The figure indicates that the maximum y2 / E1 always occurs at FD1 = 1.73, independent on the shape of the section k1, within a range of 0.874 to 0.8 for (k1 = 0 to ∞) respectively, giving a maximum value in triangular shape. The maximum hj / E1 is always at FD1 = 2.78, independent on the shape of the section k1, within a range of (0.4 for k1 = 0 to 0.5 for k1 = ∞), giving a minimum value in triangular shape, see Fig. (6). Also, since E1 increases when FD1 increases, the relative height hj/E1 tends to decrease when FD1 increases. However, it should be noted that the decreasing of hj/E1 does not mean a decreasing of y1 or y2 which are expected to increase due to the increasing of the discharge at the higher FD1. 0.6 0.5
K1 = 0
k1 = 5
k1 = 10
k1 = 20
k1 = 40
Rect.
hj / E1
0.4 0.3 0.2 0.1
y1 Yc = = E1 E min
Yc (34) Vc 2 Yc + 2g Where Vc is the critical velocity. The criteria of critical flow condition is, (Chaudhry, 2008). Vc 2 D = 2g 2 Or
y1 Yc Yc = = D E1 E min Yc + 2
(35) (36)
From the background of the hydraulic channel, the hydraulic depth D, is equal to (y and y/2) in rectangular and triangular sections respectively. Hence, Eq.36 provides a value of (2/3) and (0.8) in rectangular and triangular sections respectively. Furthermore, consider Eqs. (8 & 9) for the hydraulic depth D in trapezoidal shape, Eq.36 could be expressed as:
0.0 1
2
3
4
5
6
7
8
9
10
FD1
Fig.6: Relative height of the hydraulic jump for various trapezoidal channel shapes, k1.
Fig.5 shows that the value of y1 / E1 at FD1 = 1, is equal to 0.67 for k1= ∞ and 0.8 for k1=0, while it varies from 0.67 to 0.8 for trapezoidal sections. These results could be explained as follows: When FD1=1, the upstream depth y1 is a critical depth (Yc) and consequently E1 reduces to the minimum specific energy Emin. Therefore:
y1 Yc 2k + 4 = = E1 E min 3k + 5
(37)
Which also indicates that in case of a trapezoidal section, the ratio YC /Emin is between 4/5 for a triangular shape (k1=0) and 2/3 for a rectangular shape (k2= ∞), while it depends on the values of k in the other shapes of trapezoidal section. So, Eq.37 could be considered as a general formula to estimate the value of Yc/Emin in trapezoidal section corresponding to the section ratio k1. 59
Journal of Environmental Studies [JES] 2012. 9: 53-63
due to the increasing of the efficiency where the flow losses the most energy through the jump when FD1 > 6, (steady or strong jump). At the same time, the sequent depth is still increasing, note Fig.2. Consequently the remaining specific energy after the jump is essentially due to the sequent depth y2. Therefore, when FD1 > 6, the velocity head after the jump could be neglected and the specific energy will be estimated by the sequent depth only. In other words, E2 = y2 for FD1 > 6. 0.35 k1 = 0
0.30
k1 = 5 0.25
E2/E1 - y2/E1
Fig.7 shows the efficiency of the hydraulic jump in trapezoidal channel sections. The figure indicates that the section ratio k1, has insignificant effect when FD1 is less than 3. Also, when FD1 is grater than 10, the efficiency sustain at a constant value in a range of 73 to 80 percent corresponding to k1-value. However, in spite of that the rectangular section has a minimum efficiency corresponding to the other sections; the other shapes do not increase the efficiency higher than ten percent, which is insignificant value comparing to the difficulties of the constructions of a triangular or trapezoidal channel. Hence, practically speaking, the rectangular section could be considered more suitable section in the design of the energy dissipation structures.
k1 = 10 0.20
k1 = 40
0.15
k1 = ∞
0.10 0.05 0.00 0
1
2
3
4
5
6
7
8
9
10
11
FD1
Fig.8: The effect of FD1 on the specific energy sequent depth relationship.
100% k1=0
90%
k1=5 80%
k1=10 k1=20
(∆E) / E1
70%
k1=40
60%
Rect.
50% 40% 30% 20% 10% 0% 1
2
3
4
5
6
7
8
9
10
F D1
Fig.7: Relative losses of the hydraulic jump for various trapezoidal channel shapes, k1.
Hydraulic jump length The length of the hydraulic jump is generally measured to the downstream section at which the mean water surface attains the maximum depth and becomes reasonably level, (Philip, 2006). The length of the hydraulic jump is typically obtained from empirical functions of the jump height, based solely upon experimentation (Sturm, 2001). and the location depends on both the length and height of the jump, as well as, the upstream and downstream water surface profiles Chow (1994). Mohd (2008), drove the following differential equation to determine the jump ordinate H at known values of n, H2 and Fr1.
The analysis indicates that in case of FD1 > 6, the efficiency curve (E2/E1) tends to be asymptote to the sequent relative curve (y2 / E1), independent on the section factor k1, see Fig.8. Also, the figure shows that when k1 is grater than 10, the curves join together to a constant value for all values of FD1. This fact could be explained as follows: Based on the results of the Fig.7, the velocity after the jump is always decreased 2 1 (1 + n)(1 + nH2 + n)(1 + 2nH ) ∂H (1+ n) H −1+ (1+ n) H + 1 H (3 + 2nH ) − (3 + 2n) = 1 − 2 2 ∂ξ (1 + nH ) (1+ nH ) 3Fr12 2(1+ nH) 2H (1+ nH) H (1 + nH2 )(1 + nH ) H2 Also, AFZAL (2002). developed the x With n = 1 and ζ = (38) following model to express the length of the 2k ε y 2 hydraulic jump (Lj) in trapezoidal channel where sections. ε : universal constant for eddy kinematic Lj viscosity, independent of channel geometry. (39) = ε (1 − α ) ∆ y2 ζ : non-dimensional constant (= x /ε y2). 2 H: ordinate of jump profile (= y /y1) 4K1 K 2 ∆ = H2: sequent depth ratio (r = y2 /y1) f (ω m ) + B (39 a) (7 +32α + 41α2 +32α3 + 7α4 )M3 +12α(1+α)3 M2 (39 b) In this study, the solution of Eq.38 was f (ωm) + B = 2 / 4 2 3 provided using Runge-Kutta method to +α (41+ 74α + 41α )M +18α (1+α) determine the length of the jump at known (39 c) K 1 = M (1 + α ) + α values of k1, r and Fr1, see Fig.9. 60
Journal of Environmental Studies [JES] 2012. 9: 53-63
With M =
zy1 1 , α = 1 and ε ≈ 2 .578 = r b k1
(39 e)
Fig.9 explains a comparison between the results of Eqs. (38 & 39) and the experimental work of USBR for rectangular section and (Argyropoulous, 1961). for triangular section. The comparison shows that the results due to the model of Eqs. (39) are more precise and applicable than the results of Eq.38. Hence, the model of Eqs.39 was considered here to estimate the length of the hydraulic jump in trapezoidal channel. 9
> 4), the relation will be decreased asymptotic to a constant value, see Fig.12. That means, the maximum ratio (Lj /y2), is always near a section ratio of k1 ≈ 3 to 4, independent on the Froude number FD1. Therefore, for purposes design it is recommended to avoid this ratio in order to minimize the jump length. 13 12 11 10 9 8 Lj / y2
K 2 = 2 M (1 + α + α 2 ) + 3α (1 + α ) (39 d)
7
k1=3
6
k1=1
5
k1=0.5
4
k1=0
3 2 1 0 0
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
FD1
Fig. 10: Hydraulic jump length-Froude number relationship for k1= 0 to 3.
7 12
Eq.38, Rect. Eq.39, Rect. USBR, Rect. K=0, Eq.39 k=0, Argy.
3 1
-1
11 10 9 8 Lj / y2
Lj l y2
13
5
7 6
k1=3
5
k1=5 k1=10
4
1
2
3
4
5
6
7
8
9 10 11 12 13 14 15 16 FD1
Based on the model of Eqs.39 and depending on the solutions of Eq.18 in Table 1, the length of the jump in trapezoidal channel sections were estimated and the results prepared in the dimensionless charts of Figs. (10 & 11). The charts show that for a large value of FD1 the jump length Lj /y2 is independent on the upstream Froude number neither less the value of k1. For the rectangular shape, the results indicate that when FD1 reaches to a very high values, the jump length Lj/y2, is practically constant at approximated value of 6.9. This is because in case of a rectangular shape where M = 0, Eq.39a reduces to ∆=2.667. Consequently the term (ξ x ∆) in Eq.39 becomes 6.9. At the same time when FD1 approaches to infinity, r approaches to infinity too and α = 0 , which makes Eq.39 to give 6.9. It should be said that (Subramanya, 1998). and (Elevatorski, 1959). proposed the constant 6.9 but for FD1 > 5. In this study, when FD1 = 5, the jump length Lj /y2 is about 5.83 which indicates a difference of 17 percent. Also, the results indicate that for a constant Froude number FD1, the jump length ratio is proportional with the section factor k1 until a value of k1 between 3 to 4. After that (for k1
k1=40
2
k1= 60 k1= 100
1
Rect.
0 0
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
FD1
Fig. 11: Hydraulic jump length-Froude number relationship for k1= 3 to ∞. 13 FD1=20 FD1=15 FD1=10 FD1=5 FD1=2.77
12 11 10 Lj/y2
Fig. 9: Results of Eqs. (38 & 39), Comparing with other experimental works.
k1=20
3
9 8 7 6 5 4 0
5
10
15
20
25
30
35
40
45
50
55
60
Section Ratio, k1
Fig. 12: The effect of the section ratio k1, on the maximum length of the hydraulic jump.
Conclusions Applying the momentum conservation across a hydraulic jump in trapezoidal channel sections produced a general fourth order polynomial equation which provides a conjugate depths ratio of arbitrary cross sections. The solution was provided using Newton-Raphson method, and the results are represented as a dimensionless charts and Tables. When the values of the upstream Froude number FD1, are less than 2, the differences between the conjugate depths ratios have low significant change for all the shapes. The maximum values of y2 / E1 and hj / E1 always occur at FD1 = 1.73 and FD1 = 2.78 respectively, independent on the shape of the section (k1). When FD1 is greater than 61
Journal of Environmental Studies [JES] 2012. 9: 53-63
6, the velocity head after the jump could be neglected, (i.e. E2 = y2). The type of cross section has a little effect on the values of FD2 for FD1 > 2 and insignificant effect when FD1 is less than 2. The minimum values of FD2 for all sections range from 0.1 in triangular section to 0.15 in rectangular section, which is insignificant range. Even though, the energy dissipation efficiency of the hydraulic jump indicates that nonrectangular sections are more efficient in high Froude numbers, but these sections produce longer jumps, stability problems, and difficult in constructions. Therefore, from the hydraulic and structural point of view, the rectangular section is the preferable one in the design of hydraulic structures. Moreover, neither less of FD1, the maximum ratio of jump length (Lj / y2), always occurs when the section ratio is about k1 ≈ 3 to 4, which is recommended to avoid that for no longer jump. Nomenclature A1 & A2: Cross-sectional area before and after the jump, respectively. b: Bottom width of the sectional area. k: section ratio E1: Specific energy before the jump. E2: Specific energy after the jump Ef: jump efficiency Emin: Minimum specific energy. F: Specific force Fr: Froude number in term of the depth of flow y. FD: Froude number in term of the hydraulic depth D = A/T. g: Gravity acceleration force. H: ordinate of jump profile (= y /y1). H2: sequent depth ratio (r = y2 /y1). Lj: the length of the hydraulic jump Q: Flow rate r: Conjugate depths ratio of the initial and sequent depths, (y2 / y1) . T: Top width of the sectional area. V: Mean velocity. y1/E1: Relative initial depth. y2/E1: Relative sequent depth Yc: Critical depth. z: side slope ZC1 & ZC2: Distances of the centroids sections from the free surface area before and after the jump, respectively ∆E: Energy loss due to the jump.
ε : universal constant for eddy kinematic viscosity, independent of channel geometry. ζ : non-dimensional constant (= x /ε y2). References Argyropoulous, P.A., "The hydraulic jump and the effects of turbulence on hydraulic structure: contribution to research of the phenomenon". Proc. IX IAHR Congress, Dubrovnik, pp. 173-183., (1961). Noor Afzal & A. Bushra, "Structure of the turbulent hydraulic jump in a trapezoidal channel", Journal of Hydraulic Research, Vol. 40, (2002). No. 2. Chow, V.T., "Open channel hydraulics", McGraw-Hill, New York., (1994) Chadwick, A., Morfett, J. and Borthwick, M. (2004). "Hydraulics in civil and environmental engineering", 4th Ed. Spon Press, London. Chaudhry, Z.A. "Energy dissipation problems downstream of jinnah barrage", Pak. J. Engg. & Appl. Sci. Vol. 3 Jul (2008). (p.19 – 25). M. Hanif Chaudhry, "Open-channel flow", New York, NY 10013, USA, 2nd ed., (2008). Chanson, H. and Montes, J.S., "Characteristics of undular hydraulic jumps: Experimental apparatus and flow patterns", Journal of Hydraulic Engineering 121(2): 129-144., (1995). Chanson, H., "Bubbly flow Structure in hydraulic jump" European Jl of Mechanics B / Fluids, Vol.26,No.3,pp.367-384, DOI:10.1016 / j.euromechflu. 2006.08.001, (2007). b. Elevatorski, E.A., "Hydraulic energy dissipators". McGraw Hill, New York m,kk, (1959). Hager, W.H., "Energy Dissipators and Hydraulic Jump". Kluwer Academic Publishers, Dordrecht, The Netherlands, (1992). Hashmi, M.Z., M.Sc Thesis, "Analysis of Hydraulic Jump and Effectiveness of Energy Dissipation Devices at Jinnah Barrage", Center of Excellence Water Resources
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Journal of Environmental Studies [JES] 2012. 9: 53-63
Engineering (CEWRE), UET, Lahore, (2003). Hotchkiss, R.H., Flanagan, P.J. and Donahoo, K., "Hydraulic jumps in broken-back culverts." Transportation Research Record, 1851 35-44, (2003). Joe, D. Hoffman, "Numerical methods for engineers and scientists", 2nd ed., New York, Marcel Dekker, (2001). Modi, P.N., "Irrigation water resources and power engineering", 6th, (2004). Mohd Jamil & S A Khan, "Theoretical study of hydraulic jump in trapezoidal channel section", IE (I) Journal-CV, Volume 89, May (2008). Montes, J.S., "Disscusion of undular hydraulic jump, by V.M. Andersen", Journal Hidraulics, Division ASCE 105 (HY9): 1208-1211, (1979). Murzyn, F., and Chanson, H., "Free surface, bubbly flow and turbulence measurements in hydraulic jumps" Report No. CH63/07, Div. of Civil Engineering, The University of Queensland, Brisbane, Australia, July, 113 pages, (2007). Philip, L. Thompson and Roger T. Kilgore "Hydraulic design of energy dissipators for culverts and channels", National Highway
Institute, Technical Report, Third Edition, july, (2006). Roger Reinaur and Willi H. Hager, "Nonbreaking undular hydraulic jump", Journal of Hydraulic Research, vol.33, No.5,p.p. 683-698, (1995). Subramanya, K., "Flow in open channel". Tata McGraw Hill, New Delhi, (1998). Stahl, H. and Hager, W.H., "Hydraulic jump in circular pipes." Canadian Journal of Civil Engineering, 26 368-373, (1999). Sturm, T.W., "Open channel hydraulics", McGraw-Hill, New York, (2001). Treske, A., "Undular bores (Favre-Waves) in open channels. Experimental studies", J. Hydr. Res., 32 (3), 355370, (1994). U.S.B.R., "Hydraulic design of stilling basins and energy dissipators. Engineering Monograph" No. 35, U.S. Bureau of Reclaimation, Dept. of Interior, Washington D.C., (1958). Vatankhah, A.R. and Kouchakzadeh, S., "Discussion of solution of specific energy and specific force equations" by Amlan Das. Journal of Irrigation and Drainage Engineering, ASCE 133(4): 407–410, (2008).
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: ا $=@ذ> رA ق3B) ا: ف وD'7 اEF3 ا-. $;$"رو$#ة ا123 ا456 7* و9$: ): ،+'ا ا, ه-. دMKN ( فD'7 وا+L ,9$F ) فD'7 اEF3ت اKI E$ $;$"رو$#ة ا123 ا95 بHB :@$A 3Q F@اN ا"دي و9 اOM دMKN -= @ذج اT5) ال ا@ل وا: "3 .)61 '"أ اOM (r = y2 / y1) $;$"رو$#ة ا123 ا-3M ' A $N *H ا$': ت: >"اول و-. T5ض اM ): . س.را (FD1 and FD2) ة123" اN و9'* ود. )*) ر$* $N *H وا،*F اX$7: -. ة123ءة ا2 آZ,ود وآ. )*) ر$*و OM دMKN $;$"رو$#ة ا123@ل اQ $\: ): -= ا@ذج اF@اN .(k=b/zy) EF3 ا9 E"ى وا _$ EF3 ا9;B إنT5 اX$N "3 .]( أk=b/zy) EF3 ا9 E( و"ى واr = y2 / y1) ة123 ا-3M ' A ;@ن: +L ا9;7 ا-. 7* اF) إن اb اOM *F اX$7: -. $;$"رو$#ة ا123ءة ا2 آOM @ $`a: D "م3 -. ود. )*" ;@ن رM ة123ة ا6h -. M ;ن إهل اfN .$ اFD1 )$* I -. %١٠ "ودN Lأآ (Lj / y2) ة123" اN k اOة إ123@ل اQ ' A ن. ٣ "ودN EF3 ا9 " ;@نM .٦ -M أFD1 ة123ا اT5 اAر3 "M . FD1 ة123"م ا3 -. ود. )* ر$* OM " $b D:@ OM أO إ9 .تH اE$> -. "ا >"ا$> 3.@ا: l]:ى ا6 أ$M دراتT5A E -= ا9ا@د 63
Journal of Environmental Studies [JES] 2012. 9: 65-72 Original Paper
Morpho-Anatomical Characteristics of Olive (Olea europaea L.) Trees Leaf as Bio-indicator of Cement Dust Air Pollution in Libya A. A. El-Khatib1, D. E. M. Radwan1, A. A. Alramah-Said2 1 2
Department of Botany, Faculty of Science, Sohag University, Egypt. Department of Botany, Faculty of Science, Al-Jabal Al-Gharbi University, Libya.
Rec. 4 Nov, 2012 Accept. 23 Dec, 2012
Abstract Comparisons were made between the anatomical and morphological changes in olive tree leaves from a site with relatively clean air (Al-Khadra area), and two sites (al-Khums and Zelatin) near to cement factories in the area east to Tripoli, Libya. Olive tree leaves exhibited marked variations in their morphological and anatomical characteristics, in relations to variations in the site cement dust air pollution load. Under high pollution load, leaf visible injuries were recorded. In addition, stomata appeared in higher density and smaller size than those of control. The anatomical characteristics of olive leaf including cuticle, epidermis, palisade tissue, mesophyll tissue, and elements of vascular cylinder (xylem and phloem) reflected the deteriorate effects of cement dust air pollutants, the subject which recommend their using as bio indicators. Keywords: Olea europaea, epidermis, stomata, xylem, morphology, cement dust. Introduction Cement dust results from the grinding of a clinker, which is produced by burning a mixture of limestone, clay, and gypsum at high temperatures (1450–16001C) in specially designed kilns (Suess et al., 1985). A cement industry offers an excellent opportunity for studying the impact of dust, during the process of cement manufacture considerable amounts of dust are emitted from handling, spillage and leakages. Dust is produced from quarrying of the major raw material limestone and ending with the packing and dispatch of cement from the industry (Abdul-Wahab, 2006). Cement dust is a gray powder with an aerodynamic diameter ranging from 0.05 to 5.0 mm (Kalacic, 1973). Cement dust can cause illness by skin or eye contact as well as inhalation. Risk of injury depends on duration and level of exposure and individual sensitivity. Moreover, different cements have different ingredients. Many of them contain substances that can be hazardous, like crystalline silica (quartz), lime, gypsum, nickel, cobalt, and chromium compounds (Green N8 Residents Group, 2004). Inhalation of silica dust can cause silicosis or other potentially fatal lung diseases. In addition, inhalation of chromium compounds
found in some cement dusts can cause cancer. Hence, cement dust can be an important pathway for potential human exposure. High concentrations of particles emitted from cement plant may affect the health and property of homeowners living adjacent to the plant. There are numerous complaints about cement plant from nearby residents. They include specific problems about odors, blasting, noise, respiratory problems and corrosive dust on cars. Plant physiological parameters have been used as bio-indicators of urban habitat quality. For example, highly alkaline dustlike cement visibly injures plant leaves; even chemically inert dust physically affects photosynthesis and transpiration when it accumulates on leaf surfaces. Covering and plugging of stomata (Ricks & Williams, 1974). shading (Peirce, 1910; Thompson et al., 1984). increasing leaf temperature (Eller, 1977; Borka, 1984). and removal of cuticular wax (Eveling & Bataille, 1984; Eveling, 1984). had been used to characterize local air pollution (Moraes et al., 2002). Less attention has been given to morphological and anatomical parameters of plants as indicators of long-term responses to changing (urban) habitat quality, although parameters as specific leaf area, stomatal density and pore surface were recognized to * Corresponding author: Dr. A.A. El-Khatib
[email protected]
65
Journal of Environmental Studies [JES] 2012. 9: 65-72
vary depending on microclimatic conditions (Barber et al., 2004). Moreover, sampling and analysis of these parameters are relatively easy and inexpensive. Trees act as a sink for air pollutants and thus reduce their concentration in the air especially in urban environments (Woo and Je, 2006; Tewari, 1994; Rawat and Banerjee, 1996). Dust interception capacity of plants depends on their surface geometry, phyllotaxy, and leaf external characteristics such as hairs, cuticle, leaf shape and size, texture, length of petioles, and canopy of trees etc., weather conditions and direction and speed of wind and anthropogenic activities (El-Khatib, 2007; 2011; Santosh and Tripathi, 2008). The olive tree (Olea europaea L.) is one of the major crops in the Mediterranean region. Whilst its cultivation has spread to other regions around the world, olive production is of vital importance to the economy of Mediterranean countries, including Libya. The marked reduction in the growth and yield of olive trees in the polluted area may be explained in terms of the shading effect of the foliar cement crust as well as through the changes in soil characteristics that had been brought about by the cement factory effluents. Thus the uncontrolled emissions of a cement kiln can affect the growth of the adjacent vegetation through both the air and the soil (Khalid et al., 2009). This paper was to investigate the feasibility of using the changes in anatomical of olive tree leaves in the studied areas as bio-indicators for cement dust air pollution. Materials & Methods The study area: Three sites located in Libya were chosen for the purpose of this study. They were coastal cities located east of Tripoli, their names are Alkhums (Site I) (latitude 32º 38" N and longitude 14º 13" E), Zliten (site II) (latitude 32º 25" N and longitude 14º 29" E) and Al-khadra (Site III) (latitude 32º 26" N and longitude 13º 42" E). The two first sites are located at distance of 0.5 km from the cement factories, while the third one is located far from any pollution sources (distance of 40 km) and considered to be as control. These sites covered by olive trees as main crop, besides fragment vegetation of vegetables and wild species. As reported by
Libyan National Meteorological Center Climatologically Department, (2009), the temperature of this area is ranging between 14.66°C and 25.36°C. The annual mean of wind speed is 6.88 knots/hour, the annual mean of relative humidity is 73.17 %, and the annual mean of rain fall is 24.81 mm. Sampling At each site, leaf samples were collected from olive trees growing around the cement factories at site I and Site II, in four directions to cover the different directions of the plant load emissions as: location (1): west of the factory; location (2) north-west of the factory, location (3) south of the factory, and location (4) south-east. Sampling collection was during summer of 2010 and winter of 2011. At each location, three samples of olive tree leaves were collected, resulting in 12 leaf samples for each study site. Sampling conducted according to Lau & Luk, (2001) method. At each site, by wearing polyethylene gloves, 36 leaves were detached from each tree at 1.5-2 m above the ground by pruning shears from the outer part and inner part of the canopies and from the four directions for the tree (E, W, N, S; nine leaves per each space direction) kept in plastic bags, placed in icebox, and transported to the laboratory for the next preparation. Anatomical investigation To study the leaf anatomical structure of the studied trees, leaf samples were fixed in FAA (formaldehyde: acetic acid: alcohol, 5: 5: 90, respectively) then preserved in 70% ethyl alcohol. Transversal sections (7 µm) were obtained using microtome. The sections were stained with safranin. (0.5gm/500 ml ethyl alcohol) for 30 minutes and washed by different concentrations of ethyl alcohol (50%, 70% and 95%) then the sections stained with light green (0.5 gm/1000 ml ethyl alcohol) for 30 seconds followed by washing with 95% ethyl alcohol .The sections were mounted in canada balsam, dried at 55-60°C for 3 days and examined under light microscope (Olympus-BX51) for description of anatomical structures .The sections photographed by digital camera (Olympus –DP12) and measured by ImagePro Plus 6.1 (Ruzin, 2000).
66
Journal of Environmental Studies [JES] 2012. 9: 65-72
Polluted sites Control
Plate.1. visible injuries show that chlorosis, yellowish, necrosis and drying on the upper surface of leaves, collected from polluted sites (I and II) and control site (III) during summer and winter seasons.
Statistical Analysis: Data were subjected to statistical analysis using Minitab®14. Comparisons of means were carried out using the analysis of variance (MANOVA, Two-way). Differences were considered to be significant at level P 2ا"را إ" 5ود * ذات د B"Dإ K 8Fا"HIJت ا"LMJ> G+ه ا" NOا"+ر& و O>19و;ن دة ا" ، +آ > 2ا"را إ" 5ود ا 1" 6و> P&Jا" 1+Aو> 3ا" Qا" "JA+ ا"&; 5 Rن دة ا" . +و 2ا"را K BMا" +ت &=> OJا" Aا" " HIJت ا" " NOا"+ر& ،و> Kأ3اد أ ب 19ات " 1F L&L> ،Bو> P&Jا" ، 1+Aو> 3ا" Qا" "JA+ا"*ز " +و>VC 3ا"[ه ا"=& ا"G+ ا " G3 2!+ا"[ Aوا"[
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ا+ا>Mت VJت ا)ل ،وا K *WCا)ه ا"L+ا&ة دارة ا" 3و> رع > G3 O=1Wا" Aت ا)رد Cا"! ،و" >ا Bه dmا" Aت &> Kت وFة B 3Jو" " Oل إ" 5ا"Lة ا"K ، 3J+ *9ل >=< ،tAوز&دة G3ر; ا"*ء و> K دة O>9ا" +ور+ P3ى أداء أYء هO+N ا"+ر& وا" 3; ،O3 Kإ" 5ر P3آK Q ا"!ت ا" R1ا"=> G+م Oو 9ا"+Mت ا" W t W+& ،Oا) > hOJ GJ1إدارة ا" K B" " 3أهB G3ا" Aت B 3J> dLو. B" Bو KA& ،B AI lا"را ) Nا"-: "+ -١ه 7ه5ك =; 89ا ,ا < ; :ا>: ا'ر@? )أ!اد ا! ( ون دة ا ! ا$ت ا*رد& ا +,؟ و@ = HI5هGا ا?Fال ا? ا*ول ا*)> ا /ا- : K ) (١-١هHIJ " Qت ا" ا"LMJ> G+ه ا" NOا"+ر& )أ3اد ا"; G3 * ( 3ن دة ا" G3 +ا" Aت ا)رد Cا"! ؟ ) (١-٢ه1!" Qة Yه Nا"+ر& * ; G3ن دة ا" G3 +ا" Aت ا)رد Cا"! ؟ )(١-٣هVC +& Qم إدارة ; X1ا"Mدة G3ا" Aت ا"! ا)رد C؟ ) (١-٤ه; & +& Qن ا"Mدة؟ -٢ه 7ه5ك ا %5Iا 5$ا(ت ون دة ا ! ا$ت ا*رد& ا +,؟ و@HI5 = هGا ا?Fال ا? ا &Hا*)> ا /ا : ) (٢-١ه 1" Qو> P&Jا" 1+Aا; 5 6ن دة ا" A " +ت ا)رد Cا"! ؟ ) (٢-٢ه Q " Qا" "JA+ا"& Rا; G3 6ن دة ا" A " +ت ا)رد Cا"! ؟ أه'اف ا'را) وأه:: >]> Gأه ه dmا"را إ" 5أن 6ا>Mهت L+ا&ة G3 ا"Iآت G3 9ا"[+ة ا"" Q&> G3 QR+> ، أ" Oإ" 5أل 5 Bا" 3و>& Qا"Iآت إ"b 5آت 5 Bا" 3أو bآت 3 " B*9 آ" xت ا" cF ، +أ y 2+16ه dmا"Iآت
Journal of Environmental Studies [JES] 2012. 9: 73-81
FMCها G3إدار> ، 3 " Oوآ M+C 2Cه dmادارة ا"Mة ا"[+ق وا"=+م وا" P 3Jا"Iآت ا"1Aى G3 .O>DMوVCا " y B+==Fا" xت ا"1Aة K FMCت هة M+Cا"م وا" K 3ا" O&" K QAI> cFا"> W=C 3ل G3ا"VJت و 89 ا"R+ة .OJو" " K 3اه+ت "^VJ G3 Bت ا)ل وا"1+& G+ه ا" y1ا"1!" Rي ا"VJت G3ز&دة إ O++Cوا" K Q =+ا)W9ء و"=C Mط ا" zYإن وت. أه'اف ا'را) : ':ف ه NGا'را) إ ا*ه'اف ا -: - 1ن ا 789 6ا"; G3 3ن دة ا"G3 + ا" Aت ا)رد Cا"! +D ،د :5 أ 789 -أYء ا"NOت ا"+ر& ا" cF K ،O3ا"HIJت ا" ا"LMJ& G+وOC أYء ا" NOا"+ر& و19ا>. O ب 789 -ا" J1ا" "JA+" ++ا" ت Z > G3ا" Aت 1F cF K ،و> P&Jا" 1+A و ا" Qا" "JA+ا"&. R ج -ا 789 6ا"VC G3 3م ا"Mدة G3ا" Aت ا"! . د -ا 789 6ا"; & G3 3ن ا"Mدة. O> – ٢ف ا"را " !وج K BMا" +ت ا"Oد 3إ" };> 5أه إدارة ا". 3 }+3 - ٣ا"Mل أم ا" KJوا" G3 Kإدارات xت ا" +ا"" Gا)رد[ G3 3دة ا" x G3 +ت ا" +ا""G ا)رد. C !ت ا'را) : ; G3ء AIا"را وأK+;3 l > O+ N ر K+ K+و" B;3 QAر K+3 K+;3 B K+و 5ا" Jا"-:G"+ ا /ا? ا*و: * > D :H-1ذات د B"Dإ K 8Fا"!78 ا" O P++& G+أYء ا" NOا"+ر& )أ3اد ا" ( 3و ;ن دة ا" G3 +ا" Aت ا)رد Cا"! J +ى د(05.0 ≥ α) B"D و@/ع :5ا/ت ا /ا : ا /ا /ا*و: * > D :HO-1-2ذات د B"DإK 8F ا"HIJت ا" ا"LMJ> G+ه ا" NOا"+ر& و ;ن دة ا" +و& ;ن ا"Mدة G3ا" Aت ا)رد C ا"! + Jى د.(05.0 ≥ α) B"D ا /ا /ا: &H * > :H-1.3ذات د B"Dإ19 K 8Fة Y ه Nا"+ر& و ;ن دة ا" G3 +ا" Aت ا)رد C ا"! + Jى د(.05.0 ≥ α ) B"D ا /ا? ا: &H & D :HO-1.4ا 78!" 6ا" J1ا""JA+" ++ ا" ت ; 5ن دة ا" G3 +ا" Aت ا)رد C ا"! ، و/ع :5ا/ت ا /ا :
74
ا /ا /ا*و: & D :HO-1-2ا 1" 6و> P&Jا"5 1+A ;ن دة ا" G3 +ا" Aت ا)رد Cا"! . ا /ا /ا: &H Q " 6 & D :HO-2-2ا" "JA+ا"&5 R ;ن دة ا" +وا+د & ;ن ا"Mدة و>I "[ Oا".(Stromquist, 2000:3) X - ٢إدارة ا" : 3ه Gرة ا"[د 5ا)bء و>Lه B^8 B = G3 أو ا"=رة ا" OA +& G+ا"[د و&!OCL+ 9ا.(Wit Meyer 1998:76) B3 X -٣إدارة ا" : 3ه GC M Gو[ه و=+ات ا"[د B1I و>8رات ذه > K " BJؤDت B>FHو== Bإا> && " Bأن &M) B3ب، .(٢٠:٢٠٠٢ -٤إدارة ا" : 3ه Gا"=VJ" dت أل ا"م وا"[+ح "*AI Qت ا)ل ا"^) Yا"(٤٦:٢٠٠٢ ،G1 A -٥إدارة ا" : 3ه Gت Kا" KLوة " C1ت ا" JOوCذج " * +ت وا" ل ا"P Q+ " J ا"*AIت إ" tC 5ا" 3ا" VJ " 88!+ )ا"LJي(١٢٨:٢٠٠١، "= Fد ا"RF1ن 789 9دارة ا" 3وه-:G 8> -١غ = G3ل ا)3اد " ، M+و> M+C Q8 > + Oار. -٢إدارة ا"+I 3آ K Bآ 3ا"[Nت وا"+Mت ا Wا"!1ات ا"+Iآ . J; Q=J>-٣أو }& QAIأو BM Z +& P+M Kا" 3ا" وا" B3ا"!. 8 -٤أ+D &F OCار& إدارة و> &Wا"VJت وو O>Fو> t W+آ [ Bآ*" d1آ +ب و> }18أJ K6 > t +Aو Kا" OO3 t8و>و& OYو>= Oو O+C وا.O + J" ]O+> -٥ع K Kا)ل و 9) 3+> Dو&G^1J ا" PJ" O V3ا = K O9 J+ا"VJت وا[+Fظ ا" BVJرف أ " OYع إ"> J OآQ " O إدارة ا! : > GJدور ا"MC G3 3ح VJت ا)ل P ه Z > Q&> G3 O+ا"VJت إ" 5ا8+Dد ا""G ا" &Mا"mي ت &ف 8+د ا" ، 3وا"mي &xآ 5 رأس ا"ل ا"[Aي وا" 5 3ا"*9 K 3J+ل ا"=رات ا" K *Y3 ، &I1دوره ا" > G3ل ا"VJت إ"+M 5ت B3ا"> G+ث ا"^+ ا"mMري G3ا" P zA++" VJا" ^+ا" &O+N G3 P؛ و Kه JاآO[ &> t +م ا" 3أهcF ، 9 B أن [Oم ا" G3 3ا" م ا 5 Q+I& +DاF ا" K 9ا" Kأو آ*ه ،ا)ول I& ،إ" 5ا"M+رب ا" VJوا1+9ر ا"[;ت ا" I> G+إ"C 5ذج ; Bو>[ & O[" Bا" ،Xوآ 2Cأآ RاM>Dهت
Journal of Environmental Studies [JES] 2012. 9: 73-81
G3 bا" م ا +Dوا8+Dد& > Qإ" 5ا" M+ وا"1هن &W+" ،ا"* ا" K 11ا"^+ات وا"[Q8 &+" OJا ،O+"*=+أ ا" Q9ا"Q9 O3 ،GCR اRCDو" GMوا"+ر& ا"mي از ا"+ا K Q9ا"=ى أ O B+Dوا"mي &[ QYا"Fة 5ا"[،Q8 و&آ Lادارة 5ا" Q9ا)ول. و; Kا"O+ت ادار& 3ن هJك > G3 K&1وOت VCا" K88!+وا"+Aب &> G3ا"[Oم ا" " OC] (1998, 34ا" B3ا" JYو >19 K BJY+ات وأA3ر وOرات & O1 +Aا"[د وK ا" B3ا"Vه dا" K M>Jا" P Q[+ا" N1ا"!ر " . ) ,٢٠٠٨, MCص.(٥٩- ٥٨ أه ا! ! ا?)Fت-: Iز أه ا! ! ا?)Fت (= 9ل ( @: -١ار إICء ا" F G3 VJذا>5 b1 QAI +& B MFا" 3ا"3) F+ص اR+Dر_ ،وف ا" ق، ا"ض وا" 5 t Wا"M+Jت وا"!ت 1H ، ا" K 3Jورا> ، Oا"*ء ا"+ن و.( O>&l 3> -٢ا"& 3د ا"=ار ا)M" QRل ا"IJط ا" G " ، xا" O3 z_> G+أا" Oوارده ا"، F+ وذ"*9 K Zل ا" 3ا") +ا"Vوف ا8+Dد& ا" ،ا"D+ت ا"Mر& وا" ، +ا"J=+ت ا" ة وا".( + > -٣د Cا" 3ا" VJ+وادار& ا" F+ " ، VJو "3وآ[ءة >=م Bادارة 8> K هآ Oا" BVJ+وا"_[ و VCا" Qوا+9ر >=Jت ا)داء. -٤ا" 3ا"19 K 1 +Aات و>Mرب ا ،K&9وا"G+ > G3 6xارات إدة ا" AOوإدة ا" JOوlه K وDت ا" &W+وا" G3 K +أداء ا"VJت. t > -٥ا" 3ا" J=+وادار& ا"" F+ى ا"&&K دورا رزا G3إMCح ا" XW!+وا" ت ا +C وا" =& +وا"" وا" QR> G+ا"=ل ا" G3 Oا"Q اداري. +> -٦ج ا" VJإ" 5ا" 3ا"M+دة b1 G3ة ت ا+9ر و> 8وإ+Cج ا" Pوا"!ت و>&W ا"د .OJ اRدة ! (?)Fت ا ا: إن } W8ا"Mدة ه )س [Oم ا8+دي _O Jء 5ا" 3J+ا" GJ8وا" K G"JA+ا"ول ا" J8ا"O ، =+ف ا 1دة ا+Cج وآ =6 t ا" ق وا"+Iي ،و"+> G"+آ Lا"Mدة 5ا"[+ق وا+Dز " Jا" G3 h+Jأي Mل ،و"= >Jول ا"RF1ن G3درا>; Oع ا"Mدة و dICو" BMا"RAون، وهmا أدى إ"J> 5ع و>د ا"[&+ت ا"! mOا ا"[Oم، و Kأ[&> Obت ا"Mدة ه >& zا" Mا)& A " د ،dو " 23ا"" ا"+آ و ا1 W+ Oت (1999:507 Bonser,) .B+وف )J.M. (Juran,وز ،Bا"Mدة إ OCى * ا"h+J "*+ل .و 23ا"Mدة 5إ OCى ا"P =W ا"1 W+ت .أ ا"ا [ ا"و" =3 ISO 9000:2000 23ا"Mدة OC] :در > M 1ا"!78 75
ا"رو G3 6ا"1 W+" h+Jت ا" ،Qوف )-17 (Feignbaum, A.V. 1991ا"Mدة ]Q[> h>C :OC HIC 789ت ا" K KA& dت ا" Qور.B>1l :/( +5م اRدة: > Oد [Oم ا"Mدة إ Dأ G3 G=+ > OCأر J ر ،Bوه:G .١اRد :Nدر ا:7T/ M"3دة > V" GJا"Jس ا" ،QY[+إي >[5 B QY أ9ى. .٢اRدة :ا)9 ;Uل: >ف ا"Mدة ]) OCا"ا "*+ل( وذ") Zه ا"Mدة G3ا" 8+وا cF K B+CDا" L +ت ا"Yور& " G3ت ا"Q ا"Vه& وا") . JYا" GWواد.(٢٧٥ ٢٠٠٣ ،d (IUت IUاRدة ! اZ5ت ا : إن أه 1 W+ت > و.O=1W> G3 OC -٣ود أهاف د K B=+I ،dا+Fت ا"[Nت ا" 3O+و Gادارة وا" .O==+" K }J -٤ا" Kا" =Rو> 5 OMIأداء ا" Qو>=& ا" OJ L+دون ا" G3 Q9+اMCزا> OJ> 5+F Oا" =R G3ر أ" Oدون ار>Aب ا)W9ء. -٥ا+Dد آ Kا" z&!+وا"+ه،5[W8) t ا)8Cري(٢٠ :٢٠٠٢ ، !ا' IUاRدة ! ا ا: أن 3ا > G &W> -١ا"VJم اداري G3ا" M+C Mو;ح ا)دوار و>& ا" xو"ت. -٢اDر>=ء +ى ا"!ت ا" +ا"= " *Wب ا" 5 AJ> G+ا. O>8!b tC -٣ز&دة ا"[Aءة ا" +ور+ P3ى ا)داء "PM ا)آد& Kوادار&.K -٤ا"3ء 1 W+ت ا"*Wب وا" P+Mوا" 21ا" G وا" ل إ" 5ر;ه .
Journal of Environmental Studies [JES] 2012. 9: 73-81
K 3> -٥ا"[+ه وا"+ون وا"*ت ا C C ا" Kا" .K KA> - ٦إدارة ا" QF K Mا"*AIت "Wق ا" ا" 8وا"*9 K O Q+ل. ااءات ا" 8+وا" "F PJو.*1=+ O6 -٧ر+ P3ى ا"" Gى ا" 9 K K&[+ت ا" M *9 Kل إاز اL+"Dام VJم ا"Mدة. -٨ا"+ا Xوا" P K QA+ا)آد& Kوادار&G3 K ا" Mوا" Qوح ا"[&< ا"ا.F VC -٩م إدارة ا"Mدة ا" }J& Iا" Mا+Fا و>=&ا و ر dده BJا&.BM ) ٨٤- ٢٠٠٢:٨٣ ،Y9؛ م.(٦٧٧ :٢٠٠٥ ، (ا 7.دة ا: إن دة ا" =J> +إ" 5ة ا QFوه:G ا .ا*و F) :ا" :( =+و& O1 +ا"+ف 5ا"; Pا"= "-:cF K A اCAت ا"د& وا" &I1وا" =&Wا" O = Jا" ا". + ا .ا &W> F) : &Hو>VC B&&W> BW9 m[J [+D B bء 1 W+ت ا"Mدة *9 Kل إICء د"Q ا"Mدة وإاءا> .Oو> ت ا" Qو K BWW9اQ ;ن ا"8ل VC 5م ا"Mدة ا" Wب وذ"+" Zون G[_ Pا" Aو 6 Kا+د K dادارة ا" ا .اVC F) : HHم ا"Mدة( :و& + VCم ا"Mدة G3ا" Aت وأ Oا" و 5+FوFا>O ادار& وا"[ ، Jو>=م ا"Iآ ا"xه و Kو> ت VCم ا"Mدة. ا .اا; F) :إاد ا hواد ا"+ر&:(t G3 +& cFه dmا" Fإاد اد ا"+ر& tوا" + "! z +ا" &+ت ادار& *9ل +3ة > ر& G1 +J K BM tا"VC 5 Aم ا"Mدة )ا)&Lو (٩٠٠٢ :و> B>=1Wو&=م هDxء m[J+ا"+ر&t =1" =FDا" Kو&آ Lا"+ر& 5 tا" =&Wا"5 R اء ا"ا ا"ا. 9 ا .ا?د) F) :ا"ا ا"!ر ( 2F :أن ا" OMا"OI " Cدة >=م "ا Kا + Q ا[+ء VCم ا"Mدة "1 W+ت ا"ا [ واآI+ف DFت م ا" =Wوا>!ذ ااءات ا" 8+وا" "".O+M ا %.ا?; F) :%ا" :(79+وا" +> G+إ>م ا"ا ا"!ر Kا" OMا"OI " Cدة & +ا>!ذ ا"=ار Iن Ob }Jدة ا"Mدة ا"" )ا)&Lو G3 (٩٠٠٢ ا"" ا" " +ا [ 1) .ا"(٦٥ ،٢٠٠٤ ،KF ا'را)ت ا?; : ا'را)ت ا; : -١درا )أ ،B1ه J .(٢٨,٢٠٠٤ ،1ان ى > Z > ا 3و_ zإدارة ا" 3وأ6ه G3 3ا"&& G3 Kا"زارات ا)رد ، Cو ه 23ا"را إ" &W> 5إHرا [ه" Gأس ا"ل ا"[Aي و G3 B>CAا"Mت ،وآZ"m > &Wأدا K B=+" dا B Qو> b إدار> ،Bو> 2ا"را إ" 5ا"& Kا"، h+J أزه أن هJك * Hد& K Bا"QAI + م وا)داء ا8+Dدي أو ا. +C -٣م )ا" (٢٠٥، ١٩٩٧ ،Gرا Jان ادارة "J> ، 3و"L 2ات 8ا" 3 وا" ت1+ ،ر dا"آLة ا) J G3ء ا8+Dد ا"،GJHآ> Z"mث Kا=+CDل إ"5 8ا". 3 -٤درا )ا" ا" (٧٨,٢٠٠١ ،GCإدارة ا"" 3 وا" G+ه 23إ" 5ا"+ف 1H 5ا" 3 ا" ، VJ+وأ ،O"Abوا ،O 9و28 9 Yورة > PMIت ا" +وا"1+دل ا"G3 KأYء ا" ، VJوأآت 5أه ا"8J ا"I1ي m[J> G3ا+ا>Mت إدارة ا"، 3 و> 2إ" 5أه ا"8ب وا"=1ت Fل إدارة ا". 3 -٥أى )ا"! (٤٦,١٩٩٦ ،GM3درا Jان"ا" Q9ا" Q > G3 G3ا+9Dر ا+Dا> :GMدرا ا+9ر& J G3 Bا"K+ ا"ا " ه 23إ" 5أن هJك *Yت B&A3 B&VCو> K B=1Wأه_ Q > Oه>G ا" 3ا" VJ+وا+9Dر ا+Dا>GM و>[ ه. -٦درا أاه ا"LJي G ،و "} )J (٢٠٠٨,٢٦٨ان" إدارة رأس ا"ل ا"[Aي VJ G3ت ا)ل" cFأآ أن " 3 GO3 .789وا"mآء &ان ا"دان +ز G3أ& VJأل ،و&6xان G3ا)داء ا""G وا" VJ " G Aوه ا"اد ا"!م " BM+JC و ،B1Cوا"= ا"== " Q=C G3 KA> VJ ا" 3إ" 5وا ،Pو>=< أداء [+ق ورd >.B 3J ا'را)ت ا*I5 -١درا ) ،(Laszlo, 2002,66و ه23 ا"را إ" 6*6 };> 5أل ت Oإدارة ا" ، 3وه Gا" QMا)ول cF :رآ5 L ه ا" 3وإدار>*9 K Oل اآ +ب ا"mآء ا" "JA> G3 QR+رأس ا"ل ا"[Aي ،أ ا" QMا" :GCRرآ 5 Lا"د Kإدارة ا"+D 3اح A+ن *9 K Bل ت ا" +واA+Dر ود هmا ا" QMا"VJت ا" +و KAا" Kوا"Mت Kااع وا" C B+ا" QMا" c"Rا"mي رآ5 L
Journal of Environmental Studies [JES] 2012. 9: 73-81
اIA+ف ا" +" Q1=+آ G^1J& 5 Lأن >Aن Bإدارة ا". 3 -٢درا ) ،(Mathotra. 2003,91و ه23 ا"را إ" 5و; Pم و>& & 1J "=س ا) ل ا" ، 3وJء Cذج B 1Jوآ Z"mآ[ > &Wرات وإCAت ا"=Wع ا"م G3هmا ا"Mل 2=1H cF ،هdm ا"را G3ا"&Dت ا"+ة آLMء IC Kط ا) ا"+ة G3ا"HIJت ا +Dوا" . -٣م )(1998, 134 Brain&Newman, را Fل "Cذج إدارة ا" ،" 3و G3هdm ا"را ا+ض ا" cF1ا" ا" "QR هmا ا"Jذج +د ا"ا zوا)د ،وbد ا" 5 cF1أه دور Fة ا" ، 3وا" J ا"6xة وا+ده آ O 8Jودا G3 Cذ.B G3 -٤درا ) Mentzer & Mastunol, 2000, > (26إاء ه dmا"را & K BJ 5ي ا"b G3 zJ8ا" 3إ"BJ; 5 & O P++ا)3اد أو 3ق ا" ،Qو>1ز G3 ا"[Aءة ا" l QAI ، 8!Iر ،Gو 5 ا" VJأن >.O 3 -٦درا ) zJ (Taylor, 2000:2ا" 3أOC _ه dو; BJو& KAأن >Aن = > Y >[ Q +" G11ا"=م ث ،KوBW >=م 5ا" M+دون >[ ا"ث ا\[ر ا 'را) : >J+ول ا"را ا" MOJ z&+ا"را وإاءا>،O hOJ J& cFو P+Mو Jوأداة ا"را ،وض ا" h+Jو 6 Kا" +ت. ( R:5ا'را) : "= ا!+م ا" cF1ا" hOJا" [ Gوا"MCD G +ز هdm ا"را ،و ا+ت ا"را ا" hOJا" [*9 K Gل ا*HDع 5ا"ا Pوا"رات ا)9ى ذات ا" ، 8أ cF Kا" hOJا" =3 G +ا> 21ا"را ا" } ا"اGC وا 2!+أداة ا PM" C1+Dا" ت Kأ3اد ا" J و> L> Oه. ( K61ا789 6 ا" J1ا" "JA+" ++ا" ت ; 5ن دة ا" ، +وآ Z"mدر ا"=+رب او ا"CM+ G3إت هDxء ا" ! K61ا"[; ا" . -٤ا1+9ر *" Reliabiltyت ا"1Rت "1رات ا)داة. '+ق أداة ا'را) و::I " ف 5ق =& أداة ا"را م ا"cF1 ض ا"1رات ا"^+ O+JY> G+ات ا"را 5 K BMأYء ه Nا"+ر& "Mت ا)رد، C وآ K BM 5 Z"mا"ر Kا" ،K88!+و >
Journal of Environmental Studies [JES] 2012. 9: 73-81
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Journal of Environmental Studies [JES] 2012. 9: 73-81
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Journal of Environmental Studies [JES] 2012. 9: 73-81
Wiig, karl M. (2003, 76). "Knowledge Management Founation : Thinking sike, B. & Alan, F. (2000, 87). "The transfer of knowledge & The Retenation of Expertise: the continuing for globel assignments,journal of knowledge mgt V. (4) N (2) Stomquist, n. & Samoff, j. (2000, 3). knowledge of management system journal of comparative education, V. (30) issue (3) Taylor, R. (2000, 2). "KM" The management Process of Ensuring The Organizations Existing Knowlewdge assets Johnson, G. & Scholes, K. (1997, 34). "Exploring Corporate Strategy"4th ed., Prentice-Hall,Europe &و$e< ا8اا Cا)رد G""ا +"ا وزارة P www.mohe.gov.jo
1W" ا،( PMEC) "دارةJO"ات ا1!"ا . " ا8 &رO ، ا"=هة، CR"ا إدارةz_ و3 " ى >ا.(٢٠٠٦) ، ز&د، CرW="ا G3 K&&" ا3 G3 ه6 وأ3"ا l + " ر،" Cا"زارات ا)رد . ا)ردن، >x ،رةIJ hC " .(٢٠٠٢) ، ،ري8C) ا،F ا،5[W8 لM" اG3 O>=1W> وI"دة اM"إدارة ا t&ر+ " G" اL ا"آ،W ،" ي+"ا .h !"ي "ول ا+"ا ا"[ه: 3"( "إدارة ا٢٠٠٨) ،د1 MC ، MC IJ " دار ا"راق،" ت وا" تM>ا+Dوا . ا)ردن، ن, CR" ا1W" ا،P&ز+"وا إدارة رأس ا"ل،٢٠٠٨ }" وG ،يLJ"ا ت ا)لVJ G3 يA["ا I5* اا< ا-ب Bonser, C. (1999,36). "Total Quality Education " ،Public administration Review, No. 52. Laszlo, A-Laszlo, K. (2002, 66). " Evolving Knwledge for Development :The Role of Knowledge Management in Changing World". (JKM vol. 6).
Abstract
Following characteristics of knowledge management to achieve quality assurance of higher education Mohammad Abed Abu-qulah
The study aimed to know the effect of following some of the characteristics of knowledge to achieve the quality assurance of education "study applied to private Jordan colleges," The study indicated, there is significant statistical relationship between the activities carried out by faculty staff members and ensure the quality of education. In addition, the study indicated that a trace of computing, diversification of the library contents and provide the means of modern technology are important to ensure the quality of education. The study provided a set of recommendations, including the college offers support for the scientific activities of the faculty, and to appoint members of the owners of high expertise, and enhance and diversify the computerization of the library, and provide the necessary technological means for education.
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