Deep well cementing. Cement, additives and their temperature limitation.

1993 ◽  
Vol 58 (5) ◽  
pp. 393-396 ◽  
Author(s):  
Yoshinori Kosuge
2016 ◽  
Vol 50 (3) ◽  
pp. 227-239 ◽  
Author(s):  
Muga Yaguchi ◽  
Yoichi Muramatsu ◽  
Hitoshi Chiba ◽  
Fumiaki Okumura ◽  
Takeshi Ohba
Keyword(s):  

2013 ◽  
Author(s):  
Paolo Ferrara ◽  
Claudio Molaschi ◽  
Bill Menard ◽  
Francesca Rinaldi
Keyword(s):  

Author(s):  
M.V. Detin ◽  
◽  
D.L. Bakirov ◽  
D.N. Volokitin ◽  
G.V. Mazur ◽  
...  
Keyword(s):  

2016 ◽  
Author(s):  
Ronald T. Green ◽  
◽  
F. Paul Bertetti ◽  
Nathaniel Toll ◽  
Nicola Hill

2019 ◽  
Vol 97 ◽  
pp. 115-127 ◽  
Author(s):  
Jiandong Wang ◽  
Deng Kuanhai ◽  
Yin Zhiping ◽  
Liu Bing ◽  
Yuanhua Lin ◽  
...  

1993 ◽  
Vol 20 (1) ◽  
pp. 44-49 ◽  
Author(s):  
N. L. Powell

Abstract Foliar application of manganese and boron mixed with pesticides in water solution is a common practice for peanut (Arachis hypogaea L.) production. This study was conducted to determine the compatibility of mixing manganese, boron, and leafspot fungicides using water from three sources. Spray mixtures of the chelated manganese salt of ethylene diamine tetra-acetate and the inorganic salts of manganese as manganese sulfate(TECMANGAMTM), manganese sulfate monohydrate, manganese chloride, and manganese nitrate were developed using deep-well water, shallow well water, or distilled water. Boron was added to these mixtures using boric acid or disodium octaborate tetrahydrate. In addition, all combinations were mixed with the leafspot fungicides chlorothalonil or cupric hydroxide plus sulfur. Mixtures were equivalent to recommended rates of manganese, boron, and fungicide applied to the foliage in 140 L ha-1 of spray volume. Measurements were made of solution pH and manganese remaining in solution after filtration. Development of precipitates was noted. In the deep-well water solution (pH = 8.0), addition of manganese sulfate, manganese sulfate monohydrate and manganese chloride caused precipitates to form. Manganese nitrate and chelated manganese solutions did not form precipitates. Addition of disodium octaborate tetrahydrate increased the tank-mix pH for all waters source, and caused increased precipitation of the manganese inorganic salts, but not the chelated manganese. Use of boric acid in the water lowered solution pH, and all manganese sources remained in solution. Spray-tank-mix pH was critical in keeping all manganese inorganic salts in solution. For all pH levels studied (pH 4.6 to 8.4) the chelated manganese remained in solution without formation of a precipitate. Chemical analyses of the filtrate showed that only 75 to 80% of the inorganic salts of manganese remained in solution with disodium octaborate tetrahydrate, while 100% of the chelated manganese salt remained in solution. Inorganic salts of manganese and disodium octaborate tetrahydrate should not be mixed with chlorothalonil, and none of the manganese materials should be mixed with cupric hydroxide plus sulfur as a spray-tank-mixture for foliar application.


2014 ◽  
Vol 904 ◽  
pp. 292-295 ◽  
Author(s):  
Jian Zhao ◽  
Yi Ji Xu

Field test of particle impact drilling (PID) technology was firstly carried out in deep well and hard formation in Sichuan province china on Oct. 2013. The test formation was named Xu Jiahe, which was very difficult to penetration. Field test result shows that the ROP (rate of penetration) was nearly doubled by this technology. It indicates that there is a profound application prospect of particle impact drilling, especially for hard rock formation. In this paper, the equipment and working principle was analyzed. The experiment and simulation results showed that the rock breaking efficiency was highly increased by this technology. The details of this field test were presented too in this paper that proved the sound effect of PID.


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