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Department of Environmental Sciences, G.B. Pant University of Agriculture and Technology, Pantnagar-263 145, India. vik_singhal@rediffmail.com
The paper reports on the biogas production from water hyacinth (Eichhornia crassipes) and channel grass (Vallisneria spiralis) employed separately for phytoremediation of lignin and metal-rich pulp and paper mill and highly acidic distillery effluents. These plants eventually grow well in diluted effluent up to 40%(i.e., 2.5-times dilution with deionized water) and often take up metals and toxic materials from wastewater for their metabolic use. Slurry of the two plants used for phytoremediation produced significantly more biogas than that produced by the plants grown in deionized water; the effect being more marked with plants used for phytoremediation of 20% pulp and paper mill effluent. Biogas production from channel grass was relatively greater and quicker (maximum in 6-9 days) than that from water hyacinth (in 9-12 days). Such variation in biogas production by the two macrophytes has been correlated with the changes in C, N and C/N ratio of their slurry brought by phytoremediation.
Latest citations:
FASEB J. 2007 Jun ;21 (8):1724-9
17314136
Cit:22
Dun-Xian Tan,
Lucien C Manchester,
Paolo Di Mascio,
Glaucia R Martinez,
Fernanda M Prado,
Russel J Reiter
Department of Cellular Structural Biology, The University of Texas Health Science Center, 7703 Floyd Curl Dr., San Antonio, TX 78229, USA.
N1-acetyl-N2-formyl-5-methoxykynuramine (AMFK) is a major metabolite of melatonin in mammals. To investigate whether AFMK exists in plants, an aquatic plant, water hyacinth, was used. To achieve this, LC/MS/MS with a deuterated standard was employed. AFMK was identified in any plant for the first time. Both it and its precursor, melatonin, were rhythmic with peaks during the late light phase. These novel rhythms indicate that these molecules do not serve as the chemical signal of darkness as in animals but may relate to processes of photosynthesis or photoprotection. These possibilities are supported by higher production of melatonin and AFMK in plants grown in sunlight (10,000-15,000 microW/cm2) compared to those grown under artificial light (400-450 microW/cm2). Melatonin and AFMK, as potent free radical scavengers, may assist plants in coping with harsh environmental insults, including soil and water pollutants. High levels of melatonin and AFMK in water hyacinth may explain why this plant more easily tolerates environmental pollutants, including toxic chemicals and heavy metals and is successfully used in phytoremediation. These novel findings could lead to improvements in the phytoremediative capacity of plants by either stimulating endogenous melatonin synthesis or by adding melatonin to water/soil in which they are grown.
College of Food Science, Biotechnology and Environmental Engineering, Zhejiang Gongshang University, No. 149 Jiaogong Rd., Hangzhou 310035, China. tuyying@mail.hz.zj.cn
The potential of water hyacinth (Eichhornia crassipes) to remove a phosphorus pesticide ethion were investigated. The disappearance rate constants of ethion in culture solutions were 0.01059, 0.00930, 0.00294, and 0.00201 h-1 for the non-sterile planted, sterile planted, non-sterile unplanted, and sterile unplanted treatment, respectively, which were significantly different and implied that plant uptake and phytodegradation contributed 69% and that of microbial degradation took up 12% to the removal of the applied ethion. The accumulated ethion in live water hyacinth plant decreased by 55-91% in shoots and 74-81% in roots after the plant growing 1 week in ethion free culture solutions, suggesting that plant uptake and phytodegradation might be the dominant process for ethion removal by the plant. This plant might be utilized as an efficient, economical and ecological alternative to accelerate the removal and degradation of agro-industrial wastewater polluted with ethion.
Faculty of Engineering and Applied Science, Memorial University of Newfoundland, St John's NL, Canada. fkhan@engr.mun.ca
This paper presents an analysis of the site restoration techniques that may be employed in a variety of contaminated site cleanup programs. It is recognized that no single specific technology may be considered as a panacea for all contaminated site problems. An easy-to-use summary of the analysis of the important parameters that will help in the selection and implementation of one or more appropriate technologies in a defined set of site and contaminant characteristics is also included.
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Eco-technology Lab, Department of Environmental Sciences, GB Pant University of Agriculture and Technology, Pantnagar, India.
The present study reports on the treatment of pulp and paper mill effluent by Phanerochaete chlysosporium and the same has been compared at two different pH, 5.5 and 8.5. At both the pH, colour, COD, lignin content and total phenols of the effluent significantly declined after bioremediation. However, greater decolourisation and reduction in COD, lignin content and total phenols were observed at pH 5.5. Such bioremediated effluent of pulp and paper mill could gainfully be utilized for crop irrigation.
B Abelev,
J Adam,
D Adamová,
A M Adare,
M M Aggarwal,
G Aglieri Rinella,
A G Agocs,
A Agostinelli,
S Aguilar Salazar,
Z Ahammed,
A Ahmad Masoodi,
N Ahmad,
S A Ahn,
S U Ahn,
A Akindinov,
D Aleksandrov,
B Alessandro,
R Alfaro Molina,
A Alici,
A Alkin,
E Almaráz Aviña,
J Alme,
T Alt,
V Altini,
S Altinpinar,
I Altsybeev,
C Andrei,
A Andronic,
V Anguelov,
J Anielski,
C Anson,
T Antičić,
F Antinori,
P Antonioli,
L Aphecetche,
H Appelshäuser,
N Arbor,
S Arcelli,
A Arend,
N Armesto,
R Arnaldi,
T Aronsson,
I C Arsene,
M Arslandok,
A Asryan,
A Augustinus,
R Averbeck,
T C Awes,
J Aystö,
M D Azmi,
M Bach,
A Badalà,
Y W Baek,
R Bailhache,
R Bala,
R Baldini Ferroli,
A Baldisseri,
A Baldit,
F Baltasar Dos Santos Pedrosa,
J Bán,
R C Baral,
R Barbera,
F Barile,
G G Barnaföldi,
L S Barnby,
V Barret,
J Bartke,
M Basile,
N Bastid,
S Basu,
B Bathen,
G Batigne,
B Batyunya,
C Baumann,
I G Bearden,
H Beck,
I Belikov,
F Bellini,
R Bellwied,
E Belmont-Moreno,
G Bencedi,
S Beole,
I Berceanu,
A Bercuci,
Y Berdnikov,
D Berenyi,
A A E Bergognon,
D Berzano,
L Betev,
A Bhasin,
A K Bhati,
J Bhom,
L Bianchi,
N Bianchi,
C Bianchin,
J Bielčík,
J Bielčíková,
A Bilandzic,
S Bjelogrlic,
F Blanco,
D Blau,
C Blume,
M Boccioli,
N Bock,
S Böttger,
A Bogdanov,
H Bøggild,
M Bogolyubsky,
L Boldizsár,
M Bombara,
J Book,
H Borel,
A Borissov,
S Bose,
F Bossú,
M Botje,
B Boyer,
E Braidot,
P Braun-Munzinger,
M Bregant,
T Breitner,
T A Browning,
M Broz,
R Brun,
E Bruna,
G E Bruno,
D Budnikov,
H Buesching,
S Bufalino,
K Bugaiev,
O Busch,
Z Buthelezi,
D Caballero Orduna,
D Caffarri,
X Cai,
H Caines,
E Calvo Villar,
P Camerini,
V Canoa Roman,
G Cara Romeo,
F Carena,
W Carena,
N Carlin Filho,
F Carminati,
C A Carrillo Montoya,
A Casanova Díaz,
J Castillo Castellanos,
J F Castillo Hernandez,
E A R Casula,
V Catanescu,
C Cavicchioli,
C Ceballos Sanchez,
J Cepila,
P Cerello,
B Chang,
S Chapeland,
J L Charvet,
S Chattopadhyay,
I Chawla,
M Cherney,
C Cheshkov,
B Cheynis,
V Chibante Barroso,
D D Chinellato,
P Chochula,
M Chojnacki,
S Choudhury,
P Christakoglou,
C H Christensen,
P Christiansen,
T Chujo,
S U Chung,
C Cicalo,
L Cifarelli,
F Cindolo,
J Cleymans,
F Coccetti,
F Colamaria,
D Colella,
G Conesa Balbastre,
Z Conesa Del Valle,
P Constantin,
G Contin,
J G Contreras,
T M Cormier,
Y Corrales Morales,
P Cortese,
I Cortés Maldonado,
M R Cosentino,
F Costa,
M E Cotallo,
E Crescio,
P Crochet,
E Cruz Alaniz,
E Cuautle,
L Cunqueiro,
A Dainese,
H H Dalsgaard,
A Danu,
D Das,
I Das,
K Das,
S Dash,
A Dash,
S De,
G O V de Barros,
A De Caro,
G de Cataldo,
J de Cuveland,
A De Falco,
D De Gruttola,
H Delagrange,
A Deloff,
V Demanov,
N De Marco,
E Dénes,
S De Pasquale,
A Deppman,
G D Erasmo,
R de Rooij,
M A Diaz Corchero,
D Di Bari,
T Dietel,
S Di Liberto,
A Di Mauro,
P Di Nezza,
R Divià,
O Djuvsland,
A Dobrin,
T Dobrowolski,
I Domínguez,
B Dönigus,
O Dordic,
O Driga,
A K Dubey,
L Ducroux,
P Dupieux,
M R Dutta Majumdar,
A K Dutta Majumdar,
D Elia,
D Emschermann,
H Engel,
H A Erdal,
B Espagnon,
M Estienne,
S Esumi,
D Evans,
G Eyyubova,
D Fabris,
J Faivre,
D Falchieri,
A Fantoni,
M Fasel,
R Fearick,
A Fedunov,
D Fehlker,
L Feldkamp,
D Felea,
B Fenton-Olsen,
G Feofilov,
A Fernández Téllez,
A Ferretti,
R Ferretti,
J Figiel,
M A S Figueredo,
S Filchagin,
D Finogeev,
F M Fionda,
E M Fiore,
M Floris,
S Foertsch,
P Foka,
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E Fragiacomo,
U Frankenfeld,
U Fuchs,
C Furget,
M Fusco Girard,
J J Gaardhøje,
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A Gago,
M Gallio,
D R Gangadharan,
P Ganoti,
C Garabatos,
E Garcia-Solis,
I Garishvili,
J Gerhard,
M Germain,
C Geuna,
A Gheata,
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B Ghidini,
P Ghosh,
P Gianotti,
M R Girard,
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R Gomez,
A Gonschior,
E G Ferreiro,
L H González-Trueba,
P González-Zamora,
S Gorbunov,
A Goswami,
S Gotovac,
V Grabski,
L K Graczykowski,
R Grajcarek,
A Grelli,
C Grigoras,
A Grigoras,
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A Grigoryan,
S Grigoryan,
B Grinyov,
N Grion,
P Gros,
J F Grosse-Oetringhaus,
J-Y Grossiord,
R Grosso,
F Guber,
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C Guerra Gutierrez,
B Guerzoni,
M Guilbaud,
K Gulbrandsen,
T Gunji,
A Gupta,
R Gupta,
H Gutbrod,
O Haaland,
C Hadjidakis,
M Haiduc,
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B H Han,
L D Hanratty,
A Hansen,
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J W Harris,
M Hartig,
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A Hayrapetyan,
S T Heckel,
M Heide,
H Helstrup,
A Herghelegiu,
G Herrera Corral,
N Herrmann,
B A Hess,
K F Hetland,
B Hicks,
P T Hille,
B Hippolyte,
T Horaguchi,
Y Hori,
P Hristov,
I Hřivnáčová,
M Huang,
T J Humanic,
D S Hwang,
R Ichou,
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M Inaba,
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G M Innocenti,
P G Innocenti,
M Ippolitov,
M Irfan,
C Ivan,
V Ivanov,
M Ivanov,
A Ivanov,
O Ivanytskyi,
A Jachołkowski,
P M Jacobs,
H J Jang,
S Jangal,
M A Janik,
R Janik,
P H S Y Jayarathna,
S Jena,
D M Jha,
R T Jimenez Bustamante,
L Jirden,
P G Jones,
H Jung,
A Jusko,
A B Kaidalov,
V Kakoyan,
S Kalcher,
P Kaliňák,
T Kalliokoski,
A Kalweit,
K Kanaki,
J H Kang,
V Kaplin,
A Karasu Uysal,
O Karavichev,
T Karavicheva,
E Karpechev,
A Kazantsev,
U Kebschull,
R Keidel,
P Khan,
M M Khan,
S A Khan,
A Khanzadeev,
Y Kharlov,
B Kileng,
D W Kim,
M Kim,
S H Kim,
D J Kim,
S Kim,
J H Kim,
J S Kim,
B Kim,
T Kim,
S Kirsch,
I Kisel,
S Kiselev,
A Kisiel,
J L Klay,
J Klein,
C Klein-Bösing,
M Kliemant,
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M L Knichel,
A G Knospe,
K Koch,
M K Köhler,
A Kolojvari,
V Kondratiev,
N Kondratyeva,
A Konevskikh,
A Korneev,
R Kour,
M Kowalski,
S Kox,
G Koyithatta Meethaleveedu,
J Kral,
I Králik,
F Kramer,
I Kraus,
T Krawutschke,
M Krelina,
M Kretz,
M Krivda,
F Krizek,
M Krus,
E Kryshen,
M Krzewicki,
Y Kucheriaev,
C Kuhn,
P G Kuijer,
I Kulakov,
J Kumar,
P Kurashvili,
A B Kurepin,
A Kurepin,
A Kuryakin,
V Kushpil,
S Kushpil,
H Kvaerno,
M J Kweon,
Y Kwon,
P Ladrón de Guevara,
I Lakomov,
R Langoy,
S L La Pointe,
C Lara,
A Lardeux,
P La Rocca,
C Lazzeroni,
R Lea,
Y Le Bornec,
M Lechman,
S C Lee,
K S Lee,
G R Lee,
F Lefèvre,
J Lehnert,
L Leistam,
M Lenhardt,
V Lenti,
H León,
M Leoncino,
I León Monzón,
H León Vargas,
P Lévai,
J Lien,
R Lietava,
S Lindal,
V Lindenstruth,
C Lippmann,
M A Lisa,
L Liu,
P I Loenne,
V R Loggins,
V Loginov,
S Lohn,
D Lohner,
C Loizides,
K K Loo,
X Lopez,
E López Torres,
G Løvhøiden,
X-G Lu,
P Luettig,
M Lunardon,
J Luo,
G Luparello,
L Luquin,
C Luzzi,
R Ma,
K Ma,
D M Madagodahettige-Don,
A Maevskaya,
M Mager,
D P Mahapatra,
A Maire,
M Malaev,
I Maldonado Cervantes,
L Malinina,
D Mal'kevich,
P Malzacher,
A Mamonov,
L Manceau,
L Mangotra,
V Manko,
F Manso,
V Manzari,
Y Mao,
M Marchisone,
J Mareš,
G V Margagliotti,
A Margotti,
A Marín,
C A Marin Tobon,
C Markert,
I Martashvili,
P Martinengo,
M I Martínez,
A Martínez Davalos,
G Martínez García,
Y Martynov,
A Mas,
S Masciocchi,
M Masera,
A Masoni,
L Massacrier,
M Mastromarco,
A Mastroserio,
Z L Matthews,
A Matyja,
D Mayani,
C Mayer,
J Mazer,
M A Mazzoni,
F Meddi,
A Menchaca-Rocha,
J Mercado Pérez,
M Meres,
Y Miake,
L Milano,
J Milosevic,
A Mischke,
A N Mishra,
D Miśkowiec,
C Mitu,
J Mlynarz,
B Mohanty,
A K Mohanty,
L Molnar,
L Montaño Zetina,
M Monteno,
E Montes,
T Moon,
M Morando,
D A Moreira De Godoy,
S Moretto,
A Morsch,
V Muccifora,
E Mudnic,
S Muhuri,
M Mukherjee,
H Müller,
M G Munhoz,
L Musa,
A Musso,
B K Nandi,
R Nania,
E Nappi,
C Nattrass,
N P Naumov,
S Navin,
T K Nayak,
S Nazarenko,
G Nazarov,
A Nedosekin,
M Niculescu,
B S Nielsen,
T Niida,
S Nikolaev,
V Nikolic,
S Nikulin,
V Nikulin,
B S Nilsen,
M S Nilsson,
F Noferini,
P Nomokonov,
G Nooren,
N Novitzky,
A Nyanin,
A Nyatha,
C Nygaard,
J Nystrand,
A Ochirov,
H Oeschler,
S Oh,
S K Oh,
J Oleniacz,
C Oppedisano,
A Ortiz Velasquez,
G Ortona,
A Oskarsson,
P Ostrowski,
J Otwinowski,
K Oyama,
K Ozawa,
Y Pachmayer,
M Pachr,
F Padilla,
P Pagano,
G Paić,
F Painke,
C Pajares,
S Pal,
S K Pal,
A Palaha,
A Palmeri,
V Papikyan,
G S Pappalardo,
W J Park,
A Passfeld,
B Pastirčák,
D I Patalakha,
V Paticchio,
A Pavlinov,
T Pawlak,
T Peitzmann,
H Pereira Da Costa,
E Pereira De Oliveira Filho,
D Peresunko,
C E Pérez Lara,
E Perez Lezama,
D Perini,
D Perrino,
W Peryt,
A Pesci,
V Peskov,
Y Pestov,
V Petráček,
M Petran,
M Petris,
P Petrov,
M Petrovici,
C Petta,
S Piano,
A Piccotti,
M Pikna,
P Pillot,
O Pinazza,
L Pinsky,
N Pitz,
D B Piyarathna,
M Płoskoń,
J Pluta,
T Pocheptsov,
S Pochybova,
P L M Podesta-Lerma,
M G Poghosyan,
K Polák,
B Polichtchouk,
A Pop,
S Porteboeuf-Houssais,
V Pospíšil,
B Potukuchi,
S K Prasad,
R Preghenella,
F Prino,
C A Pruneau,
I Pshenichnov,
S Puchagin,
G Puddu,
J Pujol Teixido,
A Pulvirenti,
V Punin,
M Putiš,
J Putschke,
E Quercigh,
H Qvigstad,
A Rachevski,
A Rademakers,
S Radomski,
T S Räihä,
J Rak,
A Rakotozafindrabe,
L Ramello,
A Ramírez Reyes,
S Raniwala,
R Raniwala,
S S Räsänen,
B T Rascanu,
D Rathee,
K F Read,
J S Real,
K Redlich,
P Reichelt,
M Reicher,
R Renfordt,
A R Reolon,
A Reshetin,
F Rettig,
J-P Revol,
K Reygers,
L Riccati,
R A Ricci,
T Richert,
M Richter,
P Riedler,
W Riegler,
F Riggi,
B Rodrigues Fernandes Rabacal,
M Rodríguez Cahuantzi,
A Rodriguez Manso,
K Røed,
D Rohr,
D Röhrich,
R Romita,
F Ronchetti,
P Rosnet,
S Rossegger,
A Rossi,
C Roy,
P Roy,
A J Rubio Montero,
R Rui,
E Ryabinkin,
A Rybicki,
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K Safařík,
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P K Sahu,
J Saini,
H Sakaguchi,
S Sakai,
D Sakata,
C A Salgado,
J Salzwedel,
S Sambyal,
V Samsonov,
X Sanchez Castro,
L Sándor,
A Sandoval,
S Sano,
M Sano,
R Santo,
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J Sarkamo,
E Scapparone,
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C Schiaua,
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C Schmidt,
H R Schmidt,
S Schreiner,
S Schuchmann,
J Schukraft,
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K Schwarz,
K Schweda,
G Scioli,
E Scomparin,
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P A Scott,
G Segato,
I Selyuzhenkov,
S Senyukov,
J Seo,
S Serci,
E Serradilla,
A Sevcenco,
A Shabetai,
G Shabratova,
R Shahoyan,
N Sharma,
S Sharma,
S Rohni,
K Shigaki,
M Shimomura,
K Shtejer,
Y Sibiriak,
M Siciliano,
E Sicking,
S Siddhanta,
T Siemiarczuk,
D Silvermyr,
C Silvestre,
G Simatovic,
G Simonetti,
R Singaraju,
R Singh,
S Singha,
V Singhal,
T Sinha,
B C Sinha,
B Sitar,
M Sitta,
T B Skaali,
K Skjerdal,
R Smakal,
N Smirnov,
R J M Snellings,
C Søgaard,
R Soltz,
H Son,
M Song,
J Song,
C Soos,
F Soramel,
I Sputowska,
M Spyropoulou-Stassinaki,
B K Srivastava,
J Stachel,
I Stan,
G Stefanek,
T Steinbeck,
M Steinpreis,
E Stenlund,
G Steyn,
J H Stiller,
D Stocco,
M Stolpovskiy,
K Strabykin,
P Strmen,
A A P Suaide,
M A Subieta Vásquez,
T Sugitate,
C Suire,
M Sukhorukov,
R Sultanov,
M Sumbera,
T Susa,
A Szanto de Toledo,
I Szarka,
A Szczepankiewicz,
A Szostak,
M Szymanski,
J Takahashi,
J D Tapia Takaki,
A Tauro,
G Tejeda Muñoz,
A Telesca,
C Terrevoli,
J Thäder,
D Thomas,
R Tieulent,
A R Timmins,
D Tlusty,
A Toia,
H Torii,
L Toscano,
D Truesdale,
W H Trzaska,
T Tsuji,
A Tumkin,
R Turrisi,
T S Tveter,
J Ulery,
K Ullaland,
J Ulrich,
A Uras,
J Urbán,
G M Urciuoli,
G L Usai,
M Vajzer,
M Vala,
L Valencia Palomo,
S Vallero,
N van der Kolk,
P Vande Vyvre,
M van Leeuwen,
L Vannucci,
A Vargas,
R Varma,
M Vasileiou,
A Vasiliev,
V Vechernin,
M Veldhoen,
M Venaruzzo,
E Vercellin,
S Vergara,
R Vernet,
M Verweij,
L Vickovic,
G Viesti,
O Vikhlyantsev,
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A Vinogradov,
L Vinogradov,
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T Virgili,
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A Vodopyanov,
K Voloshin,
S Voloshin,
G Volpe,
B von Haller,
D Vranic,
G Ovrebekk,
J Vrláková,
B Vulpescu,
A Vyushin,
V Wagner,
B Wagner,
R Wan,
M Wang,
D Wang,
Y Wang,
K Watanabe,
M Weber,
J P Wessels,
U Westerhoff,
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J Wikne,
M Wilde,
G Wilk,
A Wilk,
M C S Williams,
B Windelband,
L Xaplanteris Karampatsos,
C G Yaldo,
Y Yamaguchi,
H Yang,
S Yang,
S Yasnopolskiy,
J Yi,
Z Yin,
I-K Yoo,
J Yoon,
W Yu,
X Yuan,
I Yushmanov,
C Zach,
C Zampolli,
S Zaporozhets,
A Zarochentsev,
P Závada,
N Zaviyalov,
H Zbroszczyk,
P Zelnicek,
I S Zgura,
M Zhalov,
X Zhang,
H Zhang,
F Zhou,
D Zhou,
Y Zhou,
J Zhu,
X Zhu,
A Zichichi,
A Zimmermann,
G Zinovjev,
Y Zoccarato,
M Zynovyev,
M Zyzak
Lawrence Livermore National Laboratory, Livermore, California, USA.
The ALICE Collaboration has measured the inclusive production of muons from heavy-flavor decays at forward rapidity, 2.5<y<4, in pp and Pb-Pb collisions at sqrt[s_{NN}]=2.76 TeV. The p_{t}-differential inclusive cross section of muons from heavy-flavor decays in pp collisions is compared to perturbative QCD calculations. The nuclear modification factor is studied as a function of p_{t} and collision centrality. A weak suppression is measured in peripheral collisions. In the most central collisions, a suppression of a factor of about 3-4 is observed in 6<p_{t}<10 GeV/c. The suppression shows no significant p_{t} dependence.
G.B.Pant. University of Agriculture and Technology, Udham Singh Nagar, Uttarakhand, India.
Bioligninolysis involves living organisms and/or their products in degradation of lignin, which is highly resistant, plant-originated polymer having three-dimensional network of dimethoxylated (syringyl), monomethoxylated (guaiacyl), and non-methoxylated (p-hydroxyphenyl) phenylpropanoid and acetylated units. As a major repository of aromatic chemical structures on earth, lignin bears paramount significance for its removal owing to potential application of bioligninolytic systems in industrial production. Early reports illustrating the discovery and cloning of ligninolytic biocatalysts in fungi was truly a landmark in the field of enzymatic delignification. However, the enzymology for bacterial delignification is hitherto poorly understood. Moreover, the lignin-degrading bacterial genes are still unknown and need further exploration. This review deals with the current knowledge about ligninolytic enzyme families produced by fungi and bacteria, their mechanisms of action, and genetic regulation and reservations, which render them attractive candidates in biotechnological applications.
Ecotechnology Laboratory, Department of Environmental Sciences, G.B. Pant University of Agriculture & Technology, Pantnagar, India.
The study deals with phytoextraction of Zn and Cd by Leucaena leucocephala grown on effluent fed and low nitrogen soils collected from S1, S2, and S3 sites, representing decreasing metal content with increasing distance from the effluent drain. Plant nitrogen fixation potential and soil micro-biochemical attributes against metal stress were also assessed. Increasing soil metal content and plant growth enhanced metal accumulation. Relatively greater amount of Zn than Cd was accumulated by L. leucocephala, which exceeded in roots with that of other parts. Remediation factor for Cd was maximum (3.6%) in S2 grown plant. Nodule numbers, their biomass, nitrogenase activity, and leghaemoglobin content were maximum in plants grown in S3 and minimum in S1 soil having maximum metals. Maximum soil organic C, total N, C(mic), and N(mic), respiration rate, ATP content, and enzymatic activities in response to phytoremediation was recorded in S3 followed by S2 and S1. Phytoremediation for a year enhanced extractable Zn and Cd by 36% and 45%, and their total removal by 20% and 30%, respectively from S2, which suggests the possible application of L. leucocephala for the remediation of metal contaminated sites and their fertility restoration by improving microbial functionalities and N-pool.
Role reversal during external laryngeal manipulation for tracheal intubation--an alternate approach!
Ecotechnology Laboratory, Department of Environmental Science, G.B.Pant. University of Agriculture and Technology, Pantnagar 263145, India.
Phytochelatins (PCs) are enzymatically synthesized peptides known to involve in heavy metal detoxification and accumulation, which have been measured in plants grown at high heavy metal concentrations, but few studies have examined the response of plants even at lower environmentally relevant metal concentrations. Recently, genes encoding the enzyme PC synthase have been identified in plants and other species enabling molecular biological studies to untangle the mechanisms underlying PC synthesis and its regulation. The present paper embodies review on recent advances in structure of PCs, their biosynthetic regulation, roles in heavy metal detoxification and/or accumulation, and PC synthase gene expression for better understanding of mechanism involved and to improve phytoremediation efficiency of plants for wider application.
Department of Surgery, George Eliot Hospital NHS Trust, Nuneaton, UK. singhalvik@yahoo.co.in
INTRODUCTION Appendicectomy is by far the commonest major emergency general surgical operation and laparoscopic appendicectomy is now becoming common. The question of whether a normal-looking appendix should be removed laparoscopically is more pertinent than ever before. PATIENTS AND METHODS A retrospective study was undertaken to review the histopathology results and compare macroscopic with microscopic descriptions of all patients who underwent an appendicectomy, either by open surgery or laparoscopically, over a 1-year period from 1 September 2004 to 31 August 2005. RESULTS A total of 199 appendicectomies were carried out in the year of which histopathology results for 190 could be retrieved. Of the 190 who had an appendicectomy, 110 (57.9%) were female and 80 (42.1%) were male. While appendicitis was confirmed histologically in 65 of 80 (81.2%) male patients, it could only be confirmed histologically in 57 of 110 (51.8%) female patients. However, in a large number of female patients in whom macroscopically normal appendices had been removed, other findings were noted including fibro-obliterative changes in 10, luminal inflammation in 6, serositis in 5, lymphoid hyperplasia in 3, feacoliths in 2, and pinworm in 1, making another abdominal pathology a possibility. CONCLUSIONS The number of macroscopically normal appendices removed was much larger in female patients. However in 27 of 49 normal looking appendices in females, findings such as serositis, luminal inflammation, lymphoid hyperplasia, etc. were noted on histology, suggesting that another abdominal pathology may have been missed or the appendix may still have been the cause for pain. On the basis of these findings, we suggest that diagnostic laparoscopy should be performed at least in all female patients before an appendicectomy; if no other findings are noted on laparoscopy, it is likely to be worthwhile to remove the appendix.
Ecotechnology Laboratory, Department of Environmental Science, GB Pant University of Agriculture and Technology, Pantnagar 263 145, Uttaranchal, India.
In this study, potentials of oven dried biomass of Eichhornia crassipes, Valisneria spiralis and Pistia stratiotes, were examined in terms of their heavy metal (Cd, Ni, Zn, Cu, Cr and Pb) sorption capacity, from individual-metal and multi-metal aqueous solutions at pH 6.0+/-0.1 (a popular pH of industrial effluent). V. spiralis was the most and E. crassipes was the least efficient for removal of all the metals. Cd, Pb and Zn were efficiently removed by all the three biomass. Cd was removed up to 98% by V. spiralis. Sorption data for Cr, Ni and Cd fitted better to Langmuir isotherm equation, while, the sorption data for Pb, Zn and Cu fitted better to Freundlich isotherm equation. In general, the presence of other metal ions did not influence significantly the targeted metal sorption capacity of the test plant biomasses. Ion exchange was proven the main mechanism involved in bio-sorption and there was a strong ionic balance between adsorbed (H(+) and M(2+)) to the released ions (Na(+) and K(+)) to and from the biomass. No significant difference was observed in the metal exchanged amount, by doubling of metal concentration (15-30 mg/l) in the solution and employing individual-metal and multi-metal solutions.
Ecotechnology Laboratory, Department of Environmental Science, G.B. Pant University of Agriculture and Technology, Pantnagar 263 145, India.
In present study, potentials of water hyacinth (Eichhornia crassipes) and water chestnut (Trapa bispinnosa) employed for phytoremediation of toxic metal rich brass and electroplating industry effluent, were examined in terms of biogas generation. Inability of the plants to grow in undiluted effluent directed to select 20%, 40% and 60% effluent concentrations (with deionized water) for phytoremediation experiments. Slurry of both the plants used for phytoremediation produced significantly more biogas than that by the control plants grown in unpolluted water; the effect being more pronounced with plants used for phytoremediation of 20% effluent. Maximum cumulative production of biogas (2430c.c./100gdm of water hyacinth and 1940c.c./100gdm of water chest nut) and per cent methane content (63.82% for water hyacinth and 57.04% for water chestnut) was observed at 5mm particle size and 1:1 substrate/inoculum ratio, after twenty days incubation. Biogas production was quicker (maximum from 8-12days) in water hyacinth than in water chestnut (maximum from 12-16days). The qualitative and quantitative variations in biogas production were correlated with COD, C, N, C/N ratio and toxic metal contents of the slurry used.
Anaesthesia. 2006 Apr ;61 (4):360-2
16548956
Cit:1
Department of Anaesthesiology, Sanjay Gandhi Post Graduate Institute of Medical Sciences, Lucknow 226 014, India. agarwal@sgpgi.ac.in
Venous cannulation, although a minor procedure, is often painful. The present study was planned to evaluate the efficacy of a diclofenac transdermal patch placed over the venepuncture site in decreasing the pain of cannulation. Seventy-two adults undergoing elective surgery were included in this randomised, prospective, double-blind, placebo-controlled study. Patients were divided into three equal groups. The Control group had a placebo adhesive patch placed on the both the dorsum of hand and the buttock; the Diclofenac-Buttock group had a placebo patch placed on the dorsum of the hand and a diclofenac transdermal patch on the buttock; the Diclofenac-Hand group had a diclofenac transdermal patch placed on the dorsum of hand and a placebo patch on the buttock. The patches were applied 1 h before cannulation. An 18G cannula was used for all venous cannulations. Pain during cannulation was assessed on a non-graduated 10-cm visual analogue scale. Median [interquartile range] pain scores were 3.0 [2.0-4.0] in the Diclofenac-Hand group, 5.0 [4.3-7.8] in the Diclofenac-Buttock group and 6.5 [4.5-7.0] in the Control group, p < 0.05. The numbers needed to treat were six and two in the Diclofenac-Buttock and Diclofenac-Hand groups, respectively. The application of a diclofenac transdermal patch at the cannulation site appears to be effective in decreasing cannulation pain.
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Department of Zoology, Banaras Hindu University (BHU), Varanasi, India.
Recovery of metals from the polymetallic sea nodules at the pilot plant at National Metallurgical Laboratory, Jamshedpur, India has generated a highly toxic effluent. This effluent contains several metals like Mn, Cu, Zn, Fe, Pb, Cr, and Cd that pollute the neighboring water bodies when discharged. Hence detoxification of this effluent was practiced using two plants: Lemna minor and Azolla pinnata for 7 days. During investigation A. pinnata removed 96% of Mn, 97% of Cu, 98% of Zn, 70% of Fe, 96% of Pb, 93% of Cr, 78% of Cd, and was comparatively more effective than L. minor which removed 94% of Mn, 86% of Cu, 62% of Zn, 74% of Fe, 84% of Pb, 63% of Cr, 78% of Cd. During the 7 days of experiment chlorophyll content decreased by 51% and 59% in A. pinnata and L. minor respectively. Based on our findings we can suggest that these two plants have wide range of metal retention potentialities hence can be of routine use for purification of toxic effluents.
Water Res. 2012 Jul ;46 (11):3553-62
22525457
Dept. Zoology and Entomology, Rhodes University, PO Box 94, Grahamstown 6140, South Africa. j.hill@ru.ac.za
The excessive addition of nitrogen to watersheds is recognized as one of the main causes of the global deterioration of aquatic ecosystems and an increasing number of studies have shown that δ¹⁵N signatures of macrophytes may reflect the N-loading of the system under investigation. This study investigated isotopic equilibration rates and concentration level effects of KNO₃ and cow manure nutrient solutions on the δ¹⁵N and δ¹³C signatures, C/N ratios,% N and % C of Spirodela sp. over time, to determine the feasibility of their use in monitoring anthropogenic N-loading in freshwater systems. Spirodela δ¹⁵N signatures clearly distinguished between nutrient types within 2 days of introduction, with plants grown in KNO₃ showing extremely depleted δ¹⁵N values (-15.00 to -12.00‰) compared to those growing in cow manure (14.00-18.00‰). Isotopic equilibration rates could not be determined with certainty, but plant isotopic differentiation between nutrient regimes became apparent after 2 days and started to equilibrate by day 4. Concentration level effects were also apparent, with Spirodela tissue displaying more depleted and enriched δ¹⁵N values in higher concentrations of KNO₃ and cow manure respectively. δ¹³C signatures of some plants grown in manure were more enriched than plants grown in KNO₃ and reverse osmosis (RO) water. However, nutrient induced differences in δ¹³C were small and are likely to be obscured in the natural environment. Decreased C/N ratios and increases in plant % N in zero N concentration treatments confirmed the presence of a commensal cyanobacterial-duckweed association within Spirodela sp., reducing its effectiveness as an in-situ incubator in low nutrient environments. However, indications are that Spirodela may make a useful isotope monitoring tool under conditions of long-term, continuous nutrient inputs such as systems impacted by sewage outfalls and/or wastewater inputs.
Chemosphere. 2011 Apr ;83 (5):633-46
21435676
Graduate School of Natural Science and Technology, Kanazawa University, Kakuma, Kanazawa 920-1192, Japan. aziz_ju@yahoo.com
Phytoremediation, a plant based green technology, has received increasing attention after the discovery of hyperaccumulating plants which are able to accumulate, translocate, and concentrate high amount of certain toxic elements in their above-ground/harvestable parts. Phytoremediation includes several processes namely, phytoextraction, phytodegradation, rhizofiltration, phytostabilization and phytovolatilization. Both terrestrial and aquatic plants have been tested to remediate contaminated soils and waters, respectively. A number of aquatic plant species have been investigated for the remediation of toxic contaminants such as As, Zn, Cd, Cu, Pb, Cr, Hg, etc. Arsenic, one of the deadly toxic elements, is widely distributed in the aquatic systems as a result of mineral dissolution from volcanic or sedimentary rocks as well as from the dilution of geothermal waters. In addition, the agricultural and industrial effluent discharges are also considered for arsenic contamination in natural waters. Some aquatic plants have been reported to accumulate high level of arsenic from contaminated water. Water hyacinth (Eichhornia crassipes), duckweeds (Lemna gibba, Lemna minor, Spirodela polyrhiza), water spinach (Ipomoea aquatica), water ferns (Azolla caroliniana, Azolla filiculoides, and Azolla pinnata), water cabbage (Pistia stratiotes), hydrilla (Hydrilla verticillata) and watercress (Lepidium sativum) have been studied to investigate their arsenic uptake ability and mechanisms, and to evaluate their potential in phytoremediation technology. It has been suggested that the aquatic macrophytes would be potential for arsenic phytoremediation, and this paper reviews up to date knowledge on arsenic phytoremediation by common aquatic macrophytes.
Planta. 2009 Dec ;231 (1):211-9
19898863
Cit:1
School of Life Sciences, University of Science and Technology of China, 230027, Hefei, Anhui, China.
Genes enhancing nutrient utilization efficiency are needed for crop improvement. Here, we report the isolation of a gene conferring low-sulfur tolerance from water hyacinth (Eichhornia crassipes) using a functional gene-mining method. In doing this, an entry cDNA library was constructed from the roots of nutrient-starved water hyacinth using recombination cloning and subsequently shuttled into the plant transformation- and expression-ready vector. The plant transformation- and expression-ready library was transferred into Arabidopsis and a seed library of 50,000 independent transgenic lines was generated. Three transgenic lines with enhanced low-sulfur tolerance were isolated from the seed library. One of the transgenic lines, shl143-1, with improved tolerance to sulfate deficiency and an improved root system was further analyzed. It was found that a water hyacinth jacalin-related lectin gene (EcJRL-1) was overexpressed in shl143-1. Recapitulation analysis confirmed that the overexpression of the EcJRL-1 cDNA caused the phenotype. Therefore, this study demonstrates that a jacalin-related lectin is involved in root elongation under sulfur-deficient conditions.
Jomjun Nateewattana,
Siripen Trichaiyaporn,
Maliwan Saouy,
Jintapat Nateewattana,
Prasak Thavornyutikarn,
Petch Pengchai,
Somporn Choonluchanon
Inter-department of Environmental Management (International), Hazardous Waste Management, Graduate School, Chulalongkorn University, Bangkok, Thailand. jomjun_102@hotmail.com
Mae Moh is a risky area for arsenic contamination caused by the effluent from biowetland ponds in Mae Moh lignite-fuelled power plant. The objective of this study was to investigate the arsenic concentrations of Mae Moh biowetland ponds and determine the main factors which are important for arsenic phytoremediation in the treatment system. The result revealed that arsenic concentrations in the supernant were in the range of less than 1.0 microg As L(-1) to 2.0 microg As L(-1) while those in the sediment were in the range of 25-200 microg As kg soil(-1). Both values were below the Thailand national standard of 0.25 mg As L(-1) for water and 27 mg As kg soil(-1) for the soil. Arsenic accumulation in the biomass of 5 aquatic plants at the biowetland ponds ranged from 123.83 to 280.53 mg As kgPlant(-1). Regarding the result of regression analysis (R (2)= 0.474 to 0.954), high concentrations of organic matter and other soluble ions as well as high pH value in the sediment could significantly enhance the removal of soluble arsenic in the wetland ponds. From the regression equation of accumulated arsenic concentration in each aquatic plant, Eichhornia crassipes (Mart.) Solms.(R (2)= 0.954), Ipomoea aquatica Forsk.(R (2)= 0.850), and Typha angustifolia (L.)(R (2)= 0.841) were found to be preferable arsenic removers for wastewater treatment pond in the condition of low Eh value and high content of solid phase EC and phosphorus. On the other hand, Canna glauca (L.)(R (2)= 0.749) appeared to be favorable arsenic accumulator for the treatment pond in the condition of high Eh value and high concentration of soluble EC.
Environmental Sciences (FEBES), Mizoram University, Tanhril, Aizawl, Mizoram, India. prabhatrai24@yahoo.co.in
Aquatic pollution poses a serious challenge to the scientific community worldwide, since lakes or reservoirs find multifarious use and most often their water is used for drinking, bathing, irrigation, and aquaculture. Nine metals and several physicochemical parameters, from four sampling sites in a tropical lake receiving the discharges from a thermal power plant, a coal mine, and a chlor-alkali industry, were studied from 2004 to 2005. Pertaining to metal pollution, the site most polluted with heavy metals was Belwadah, i.e., waters and sediments had the highest concentration of all the metals examined. The reference site was characterized by the presence of low concentrations of metals in waters and sediments. Following the water quality monitoring, 2-month field phytoremediation experiments were conducted using large enclosures at the discharge point of different polluted sites of the lake. During field phytoremediation experiments using aquatic macrophytes, marked percentage reduction in metals concentrations were recorded. The percentage decrease for different metals was in the range of 25% to 67.90% at Belwadah (with Eichhornia crassipes and Lemna minor), 25% to 77.14% at Dongia nala (with E. crassipes, L. minor and Azolla pinnata), and 25% to 71.42% at Ash pond site of G.B. Pant Sagar (with L. minor and A. pinnata). Preliminary studies of polluted sites are useful for improved microcosm design and for the systematic extrapolation of information from experimental ecosystems to natural ecosystems.
Department of Forest Ecology, Biodiversity and Environmental Sciences, Mizoram University. prabhatrai24@yahoo.co.in
The level of heavy metal pollution in Singrauli, an industrial region in India, was assessed and the phytoremediation capacity of a small water fern, Azolla pinnata R.BR (Azollaceae), was observed to purify waters polluted by two heavy metals, i.e., mercury (Hg) and cadmium (Cd) under a microcosm condition. Azolla pinnata is endemic to India and is an abundant and easy-growing free-floating water fern usually found in the rice fields, polluted ponds, and reservoirs of India. The fern was grown in 24 40-L aquariums containing Hg2+ and Cd2+ ions each in concentrations of 0.5, 1.0, and 3.0 mgL(-1) during the course of this study. The study revealed an inhibition of Azolla pinnata growth by 27.0-33.9% with the highest in the presence of Hg (II) ions at 0.5 mgL(-1) in comparison to the control After 13 days of the experiment, metal contents in the solution were decreased up to 70-94%. In the tissues of Azolla pinnata, the concentration of selected heavy metals during investigation was recorded between 310 and 740 mgKg(-1) dry mass, with the highest levelfoundfor Cd (II) treatment at 3.0 mgL(-1) containing a metal solution.
Biotechnology Department, SIES-Indian Institute of Environment Management, Sri Chadrasekarendra Saraswati Vidyapuram, Sector V, Nerul, Navi Mumbai 400 706, India.
Water hyacinth (Eichhornia crassipes), an aquatic weed common to the subtropic/tropical regions, was utilized as an inexpensive lignocellulosic substrate for production of cellulase by Trichoderma reesei. The effects of process parameters like substrate pretreatment, substrate concentration, initial medium pH, mode of inoculation, and incubation temperature on cellulase production were investigated. Under optimal conditions, a maximal cellulase activity of 0.22 +/- 0.04 IU/ml (approximately 73.3 IU/g cellulose) was recorded at the end of 15-day incubation period. Specific activity of the enzyme was 6.25 IU/mg protein. Hydrolysis of 1% substrate (water hyacinth) using crude enzyme dosage of 1.2 IU/g water hyacinth showed 28.7% saccharification in 1 h. The observations in present study indicate that saccharification of cellulose from water hyacinth was significantly higher by laboratory-produced cellulase than the commercial blend.
Forest Ecology Biodiversity and Environmental Sciences, School of Earth Sciences and Natural Resource Management, Mizoram University, Tanhril, Aizawl, 796001, India. prabhatrai24@yahoo.co.in
Concentrations of heavy metals (Cu, Cr, Fe, Pb, Zn, Hg, Ni, and Cd) and macronutrients (Mn) were measured in industrial effluents, water, bottom sediments, and wetland plants from a reservoir, Govind Ballabh (G.B.) Pant Sagar, in Singrauli Industrial region, India. The discharge point of a thermal power plant, a coal mine, and chlor-alkali effluent into the G.B. Pant Sagar were selected as sampling sites with one reference site in order to compare the findings. The concentrations of heavy metals in filtered water, sieved sediment samples (0.4-63 microm), and wetland plants were determined with particle-induced X-ray emission. The collected plants were Aponogeton natans, L. Engl.& Krause, Cyperus rotundus, L., Hydrilla verticillata,(L.f.) Royle, Ipomoea aquatica, Forssk., Marsilea quadrifolia, L., Potamogeton pectinatus, L., Eichhornia crassipes,(Mart.) Solms Monogr., Lemna minor, L., Spirodela polyrhiza (L.) Schleid. Linnaea, Azolla pinnata, R.Br., Vallisneria spiralis, L., and Polygonum amphibium, L. In general, metal concentration showed a significant positive correlation between industrial effluent, lake water, and lake sediment (p < 0.01). Likewise, significant positive correlation was recorded with metals concentration in plants and lake ambient, which further indicated the potential of aforesaid set of wetland macrophytes for pollution monitoring.
Ultrasonics. 2009 Feb ;49 (2):153-8
18951602
Department of Civil and Environmental Engineering, Technion, Israel Institute of Technology, Haifa 32000, Israel. kfelix@tx.technion.ac.il
The capacity of floating aquatic plants to purify sewage effluents drops rapidly as a result of biofouling processes that occur on the plant roots. This is due to the high concentration of microorganisms (MO) present in the wastewater. The possibility to apply low frequency (20 kHz) in sonification was examined under laboratory conditions. The ability of US to remove MO from the roots was studied using commercially available sonicators at intensity levels ranging from 2.7 W/cm(2) to 81.4 W/cm(2),(corresponding power levels ranging from 75 W to 500 W) while varying application periods between 5 and 60 min. The results show that MO can be removed effectively (up to 98%) by exposing the Eichhornia crassipes roots to US for 5 min at the intensity level of 64.5 W/cm(2). The efficiency of the wastewater treatment increased with exposure time and power input. The study proved that the US treatment is effective in removing MO that otherwise adhere to the roots, by more then two orders of magnitude.
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