scholarly journals The effect of pH on the uptake of zinc and cadmium in marine phytoplankton: Possible role of weak complexes

2012 ◽  
Vol 57 (1) ◽  
pp. 293-304 ◽  
Author(s):  
Yan Xu ◽  
Dalin Shi ◽  
Ludmilla Aristilde ◽  
François M. M. Morel
2010 ◽  
Vol 39 (10) ◽  
pp. 2262-2267 ◽  
Author(s):  
Raul Franzolin ◽  
Burk A. Dehority

In order to study the effect of pH on defaunation in the rumen, four rumen fistulated steers were fed a basal roughage diet for a 4-week adaptation period followed by 17 weeks of feeding with three diets and two feeding levels of high concentrate diet. Rumen outflow fluid rate was evaluated in both ration levels. Rumen protozoa population was monitored weekly and when animals became defaunated, protozoa were reinoculated with rumen contents from one of the faunated steers. At every two weeks, during all the experimental period, rumen pH was measured in all animals at 0, 4, 8 and 12 h after feeding. It was observed an individual animal influence on the establishment and maintenance of the rumen ciliate protozoa population. In all sampling times, mean rumen pH values were higher in faunated steers than in the defaunated ones. No differences were observed in rumen outflow fluid rates between the two ration levels. Extended periods of low rumen pH are probably more detrimental to the survival of ciliate protozoa in the rumen than other factors.


2020 ◽  
Vol 26 (12) ◽  
pp. 6787-6804
Author(s):  
Miriam Seifert ◽  
Björn Rost ◽  
Scarlett Trimborn ◽  
Judith Hauck

2006 ◽  
Vol 253 (2) ◽  
pp. 502-509 ◽  
Author(s):  
A.S. Akhtar ◽  
D. Susac ◽  
P.C. Wong ◽  
K.A.R. Mitchell
Keyword(s):  
Al Alloy ◽  

2012 ◽  
Vol 43 (11) ◽  
pp. 1599-1613 ◽  
Author(s):  
Mengmeng Zhang ◽  
Jia Liu ◽  
Chengyu Tian ◽  
Renqing Wang ◽  
Jiulan Dai
Keyword(s):  

1985 ◽  
Vol 55 (12) ◽  
pp. 766-773 ◽  
Author(s):  
Y.K. Kamath ◽  
S.B. Hornby ◽  
D. Bergeron ◽  
H.-D. Weigmann

2016 ◽  
Vol 67 (1) ◽  
pp. 85-98 ◽  
Author(s):  
Önder İdil ◽  
İkbal Macit ◽  
Özge Kaygusuz ◽  
Cihan Darcan

1983 ◽  
Vol 40 (S2) ◽  
pp. s192-s196 ◽  
Author(s):  
James G. Sanders

Biological mediation of arsenic speciation in marine systems is substantial and significant. Phytoplankton reduce and methylate arsenic, thus altering its geochemical cycle. Rates of arsenic reduction and methylation are proportional to the primary productivity of the ecosystem. In highly productive ecosystems, up to 80% of the total arsenic pool may undergo reduction and methylation. Experiments detailing rates of reduction have been performed in controlled marine ecosystems. Predictions of arsenic speciation based on these results agree well with actual samples taken from coastal areas. The form of reduced arsenic present varies between regions and temporally within regions, probably because of differences in phytoplankton community structure.


Author(s):  
Ciro A. Rosolem ◽  
Antonio P. Mallarino ◽  
Thiago A. R. Nogueira

AbstractPotassium (K) is found in plants as a free ion or in weak complexes. It is easily released from living or decomposing tissues, and it should be considered in fertilization programs. Several factors affect K cycling in agroecosystems, including soil and fertilizer K contributions, plant K content and exports, mineralization rates from residues, soil chemical reactions, rainfall, and time. Soil K+ ions can be leached, remain as exchangeable K, or migrate to non-exchangeable forms. Crop rotations that include vigorous, deep-rooted cover crops capable of exploring non-exchangeable K in soil are an effective strategy for recycling K and can prevent leaching below the rooting zone in light-textured soils. The amount of K released by cover crops depends on biomass production. Potassium recycled with non-harvested components of crops also varies greatly. Research with maize, soybean, and wheat has shown that 50–60% of K accumulated in vegetative tissues is released within 40–45 days. A better understanding of K cycling would greatly improve the efficacy of K management for crop production. When studying K cycling in agricultural systems, it is important to consider: (1) K addition from fertilizers and organic amendments; (2) K left in residues; (3) K partitioning differences among species; (4) soil texture; (5) soil pools that act as temporary sources or sinks for K. In this chapter, the role of cash and cover crops and organic residues on K cycling are explored to better understand how these factors could be integrated into making K fertilizer recommendations.


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