Coffee Economics the Role of Coffee in Economic Development

Coffee Economics: The Role of Coffee in Economic Development Contents INTRODUCTION Purpose of Report Scope of report Definitions Background International Coffee Trade Price Stabilization in the Coffee Economy The International Coffee Organization International Coffee Agreements Labor Technology in Coffee Production Summary Conclusions References Figures Tables Figure 1. Map of production r: cultivation of Coffea Robusta, m: cultivation of Coffea Robusta and Coffea Arabica., a: cultivation of Coffea Arabica. Figure 2. Green coffee bean cash and future price from 1995 - 2005 Source: Leibtag et al., 2007, p. 2 Table 1. Coffee†¦show more content†¦(Source: Wikipedia 2008) International Coffee Trade â€Å"Coffee price and coffee-price terminology change along the market chain. The price that a consumer faces at a supermarket or other food retailer is termed the ‘retail price,’ the price charged by coffee manufacturers to retailers and wholesalers is the ‘manufacturer price,’ and the price of green coffee beans on commodity exchanges is the ‘commodity price’ or ‘commodity cost’.† (Leibtag et al., 2007, p. 1) Although this report deals primarily with commodity prices, it is important to note the large number of transactions that take place from grower to the final retail market. Historically, the commodity price of coffee has been extremely volatile due to both supply shocks (like poor crops, bumper crops, and new competition) and demand shocks (like changes in consumer tastes, and consumer unease regarding the health effects of coffee consumption). Figure 2 shows a clear example of the volatility of the commodity prices for coffee over a ten-year period. Figure 2 â€Å"also shows the behavior of coffee futures prices over the last 10 years from the [New York Board of Trade] NYBOT. Coffee futures indicate the expectations of market participants.† (Leibtag et al., 2007, p. 3) [pic] Figure 2. Green coffee bean cash and future price from 1995 - 2005 The futures prices in figure [2] are for prices 13 months in advance. Source: Leibtag et al., 2007, p. 2 PriceShow MoreRelatedDescribe the different roles in a business buying center. Then outline which individuals might play those roles in the process of buying food for a school cafeteria.1672 Words   |  7 PagesA.Describe the different roles in a business buying center. Then outline which individuals might play those roles in the process of buying food for a school cafeteria. Buying centers have numerous of roles of participation in the purchasing decision process. There are users who are the people who actually use the goods and services. 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Machine Learning - 2512 Words

1. Introduction Humans can expand their knowledge to adapt the changing environment. To do that they must â€Å"learn†. Learning can be simply defined as the acquisition of knowledge or skills through study, experience, or being taught. Although learning is an easy task for most of the people, to acquire new knowledge or skills from data is too hard and complicated for machines. Moreover, the intelligence level of a machine is directly relevant to its learning capability. The study of machine learning tries to deal with this complicated task. In other words, machine learning is the branch of artificial intelligence that tries to find an answer to this question: how to make computer learn? When we say that the machine learns, we mean that†¦show more content†¦For example, classification algorithms which assign instances to the predefined classes requires supervised learning systems. There are also many other subcategories of supervised learning systems according to learning strategies. One of them is rote learning and direct implanting of new knowledge. In this category there is no inference or transformation of the data. All the required knowledge for a machine to learn is created during the programming or directly given as facts within the primitive database by a programmer or a user. Learning from instruction is another subcategory of supervised learning. The system gets the required knowledge as structured input from a teacher. Teacher can be many things such as a human or a textbook. In this case, although the system is supposed to be able to make some inferences, the large part of the burden remains with the instructor. Learning from instruction is very similar to the learning of a student from a teacher in real life, therefore many methods used in this subcategory parallels with formal education methods. Another subcategory of supervised learning is learning by analogy. 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God and The Common Good Approach Allowing Evil to Demonstrate Empathy Free Essays

When one looks at the atrocities in the world today and the example used by Johnson of the innocent infant burned in a building, a common reaction is empathy and sympathy. If Johnson insists on viewing God as a mortal and asserting that a human being would not allow such atrocity, then it is useful to look at approaches taken by ethical, moral actors in the world today. Looking at the Common-Good approach, we may assert that in order for us to have qualities, such as empathy, compassion, and other redeemable traits, we must have situations in our lives that evoke these qualities. We will write a custom essay sample on God and The Common Good Approach : Allowing Evil to Demonstrate Empathy or any similar topic only for you Order Now Without pain and suffering, there is no need for these positive traits, therefore, the argument that God is not good does not apply. His position is to ensure that men can become good of their own free will. Johnson would argue this approach equates to allowing men to become evil on their own free will, as well. But, this is the essence of free will and of the Common-Good approach, we must be able to see both good and evil to decide how to best achieve a society that can combat this inevitability of free will. Therefore, God can be looked at as human, then human approaches to ethics and the common good must be utilized, so under the Common Good approach, God is good. The Common Good approach essentially deals with an idea that individual good is equated and ensured with public good and that individual, honorable traits should be shared as a community in a healthy fashion. In this way, goodness, is not good if it is not shared. To apply this to counteract Johnson’s argument, it can be said, then, that in order to recognize good to share it, we must also be able to recognize bad or â€Å"evil†, in order to know how to counter it in a world of free will. â€Å"Appeals to the common good urge us to view ourselves as members of the same community, reflecting on broad questions concerning the kind of society we want to become and how we are to achieve that society† (Velasquez, et al, 1996, 2). Johnson’s argument to this would be that just as there is an imagined God that promotes good in the actions of man in reference to free will, there could easily be an evil God that does the opposite. â€Å"For example, we could say that God is evil and that he allows free will so that we can freely do evil things, which would make us more truly evil than we would be if forced to perform evil acts† (Johnson, 1983, 88). This argument against free will does not compliment Johnson’s insistence that we look at God as a human being. Just as societies and groups strive to make communities better, there are groups, who conspire to do evil deeds and go against the common good. If God is only human, then God can only hope that others will chose not to do evil with their free will. In conclusion, Johnson is flawed in looking at God as if God is human, then attaching inhuman traits or superhuman traits to action or inaction. If God is made of human qualities, then there will be flaws in even God’s own self and design. But, with the insistence of Johnson to claim God as human, then we can simply look at ethical human approached to good and evil. We can be hopeful that with the Common Good approach that moral actors will do what is right with the idea that God would act in this same manner. References Johnson, B. C. â€Å"The Problem of God and Evil† in The Atheist Debater’s Handbook. (1983). Amherst, NY: Prometheus Books. 99-108. reprint. Velasquez, M. , Andre, C. , Shanks, T, Meyer, S. J. Meyer M. â€Å"Thinking Ethically: A Framework for Moral Decision Making† in Issues in Ethics (Winter, 1996). 2-5. How to cite God and The Common Good Approach : Allowing Evil to Demonstrate Empathy, Papers

Black Panthers Essay Research Paper free essay sample

Black Panthers Essay, Research Paper . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; . ; ; Use of Nitrogen as a Fertilizer In 1898, the president of the British Association for the Advancement of Science, Sir William Crookes, startled a distinguished scientific audience when he declared during his presidential reference that # 8220 ; England and all civilised states stand in deathly hazard of non holding plenty to eat. # 8221 ; The deathly hazard that Sir William foresaw was the inability of husbandmans to fulfill the increasing demand for nutrient given current supplies of N. At the clip of Sir William # 8217 ; s reference, the chief beginnings of N fertilisers were sodium nitrate and ammonium sulfate. Sodium nitrate was obtained from huge sedimentations of nitrate-bearing stones, called hardpan, that had been discovered in Chile at the beginning of the 19th century. Ammonium sulphate was obtained from coal gas. Other beginnings of N included sewerage, guano ( bird dungs ) , and manure, but these were of worsening importance. Sir William suggested that to run into the universe # 8217 ; s increasing N demands, chemists must develop methods for unnaturally repairing atmospheric N. A successful response to this challenge was made by the German scientist Fritz Haber. Haber created a method for synthesising ammonium hydroxide from N and H, which was later developed into an industrial procedure by the industrial chemist Carl Bosch and became known as the Haber-Bosch method. At the beginning of the First World War, the estimated universe one-year production of N fertilisers was about 0.6 million dozenss, compared to universe production of 2.5 and 1.0 million dozenss of P and K fertilisers, severally. Today, chiefly because of the Haber- Bosch procedure, this tendency has been reversed. Presently, the United States entirely yearly produces about 12 million dozenss of N fertilisers, compared with 10 million dozenss of P and merely 2 million dozenss of K fertilisers. With today # 8217 ; s high inputs of N fertilisers, American husbandmans routinely achieve degrees of harvest productiveness that would hold seemed unlikely to Sir William Crookes and his fellow scientists. In the past 50 old ages, for illustration, the mean one-year outputs of maize in the United States have increased by a factor of four or five. This progress in agricultural productiveness, and the fertiliser usage upon which it depends, is indispensable if the universe # 8217 ; s population is to be sustained. Unfortunately, these additions have incurred environmental costs ; some N applied to harvests flights to land and surface Waterss, sometimes with detrimental effects. Nitrogen in Plants, Soil, and Groundwater Good harvest outputs depend on an equal supply of N. Most nonlegume harvests require added N to accomplish the outputs required today. Missing sufficient N, workss normally become xanthous and stunted, with smaller than mean flowers and fruits. For illustration, grain harvests grown with unequal N produce a hapless output with low protein content. Without N fertilisers, an estimated tierce of our current agricultural production would be lost. Under most conditions, nevertheless, husbandmans supply more than twice the N required by a harvest to accomplish the best outputs. Unfortunately, much of the applied N is nomadic in dirt and may be carried to groundwater, perchance polluting imbibing H2O supplies. ( See Cornell Cooperative Extension Fact Sheet 400.02, Nitrate Health Effects in Drinking Water, for a treatment of this issue. ) Understanding the chemical science of N in dirts can assist husbandmans provide sufficient N for harvest demands without losing inordinate sums to implicit in groundwater. Forms of Soil Nitrogen. Nitrogen occurs of course in many signifiers. In the dirt, it exists in two major categories of compounds: Organic N, such as proteins, aminic acids, and urea, including N found within life beings and disintegrating works and animate being tissues. Inorganic N, including ammonium ( NH4+ ) , ammonia gas ( NH3 ) , nitrite ( N02 ) , and nitrate ( N03 ) . Within these two signifiers, there are many different N compounds. Some are soluble and others are comparatively indissoluble ; some are nomadic in dirt and others are immobile ; and some are available for works consumption and others are non. Nitrogen in dirt is continually being transformed among these assorted signifiers through a complex web of physical, chemical, and biological reactions jointly called the N rhythm. The Nitrogen Cycle. The nitrogen rhythm in dirt includes the undermentioned procedures, in which microbes play a important function ( fig 1. See fact sheet ) : Arrested development. Ninety per centum of the Earth # 8217 ; s N is in the ambiance in the signifier of dinitrogen gas ( N2 ) . Gaseous N is chemically stable and unserviceable by most biological beings. Some species of bacteriums absorb atmospheric dinitrogen gas and change over it into ammonium, which workss can utilize. This procedure, called N arrested development, is the chief natural agencies by which atmospheric N is added to the dirt. Mineralization. As works and other organic residues decompose, N is converted to ammonium by dirt micro-organisms through a procedure known as mineralization. Plant roots absorb some of the ammonium, and some is chemically converted to gaseous ammonium hydroxide and lost to the ambiance. Nitrification. Bacteria transform the ammonium in the dirt to nitrite and so to nitrate in a sequence of stairss called nitrification. Plant consumption. Nitrate is a negatively charged anion and hence normally remains in the dirt H2O instead than being adsorbed to dirty atoms. Plants readily absorb nitrate through their roots and utilize it to bring forth protein. Leaching. The nitrate non captured by works roots is free to travel with dirt H2O. This can ensue in important leaching, or motion of the nitrate to deeper dirt deepnesss. Denitrification. Where there is a shortage of O in the dirt, called an anaerobiotic status, some bacteriums meet their energy demands by cut downing nitrate to dinitrogen gas or to nitrogen oxide ( N2O ) . This biological procedure is called denitrification. It consequences in a loss of N from the dirt and the return of N to the ambiance. Destiny of Nitrogen in the Field In the dirt of any farm field, N is in a uninterrupted province of flux. Losses occur when harvests are removed for farm animal provender or human nutrient, which frequently is consumed far from the land on which it was produced. Surface overflow and attendant dirt eroding can besides do important losingss of dirt N. Other losingss occur through volatilization of ammonium hydroxide and leaching or denitrification of nitrate. Three types of inputs can counterbalance for N losingss in farm Fieldss: ( 1 ) fertilisation, ( 2 ) N arrested development by leguminous plants, and ( 3 ) supplementation with manure or other organic affair high in N. Farm direction of dirt N depends on an apprehension of these inputs and end products so that harvest demands can be adequately met without inordinate N losingss to the environment. Gaseous Losingss of Nitrogen. In cultivated Fieldss, N is converted into gas and released into the ambiance in two ways. First, when urea and ammonium signifiers of fertilisers ( such as anhydrous ammonium hydroxide, ammonium nitrate, ammonium sulphate, and ammoniated phosphates ) are deposited on moist surfaces, they may undergo a series of chemical transitions to ammonia. The ammonium hydroxide gas so escapes to the ambiance instead than going a works food. This loss, termed volatilization, is reduced if the fertiliser is washed into the dirt by rain or irrigation or if the fertiliser is drilled into the dirt to a deepness of an inch or more. The 2nd path by which N is lost to the ambiance is through denitrification. If pockets in the dirt become saturated with H2O so that O is excluded, denitrifying bacteriums can cut down the nitrate to dinitrogen or nitrogen oxide gas. Poorly drained and heavy dirts are peculiarly prone to denitrification, and a significant sum of applied N may be lost to the ambiance. In some nonagricultural instances, denitrification is good. In infected armored combat vehicles and leaching Fieldss, for illustration, denitrification releases nitrogen to the air as a gas, cut downing the sum of nitrate available for possible taint of land and surface Waterss. Conversion of Nitrogen to a Plant-Available Form. Merely inorganic N can be absorbed by workss. The greater portion of N in the field, nevertheless, is normally in organic signifier such as proteins and aminic acids. Under normal conditions in the Northern hemisphere, merely about 2 or 3 per centum of the organic N in dirt is converted to inorganic N each twelvemonth. The natural decay of organic affair provides a slow but uninterrupted supply of N, which tends to be taken up by workss instead than lost to the ambiance or to H2O. Legumes can supplement dirt N supplies by repairing N from the ambiance. This is accomplished by nitrogen-fixing bacteriums populating in nodules on the works roots. Leaching of Nitrate. Nitrate does non adsorb strongly to dirty atoms. If non taken up by workss, nitrate will be either denitrified or carried below the root zone, possibly to groundwater. Factors that determine whether nitrate will make groundwater include: the sum of nitrate in the dirt, the measure and timing of rainfall or irrigation, the dirt # 8217 ; s capacity to keep H2O, the presence and denseness of workss, the rates of infiltration and infiltration of H2O through the dirt, the rate of evapotranspiration relation to precipitation and irrigation, and the dirt temperature. In the eastern United States, the chance for nitrate leaching is greatest in early spring and in the autumn. Rainfall tends to be frequent and heavy during these seasons, and the low rates of works growing and evapotranspiration license more of the added H2O to leach downward to groundwater. Plant consumption of dissolved foods besides is low during these periods, so leaching losingss tend to be high. Soil type is a major factor act uponing the grade to which nitrate is lost to groundwater. Sandy or other really good drained dirts are most vulnerable to leaching losingss. Farmers can make small to alter the character of the dirts in their Fieldss. Likewise, they have no control ove r the vagaries of the conditions. What, so, can husbandmans make to conserve a valuable harvest food while minimising nitrate taint of groundwater? Fertilize Crops, Not Groundwater To utilize fertiliser N right, take the undermentioned stairss for nonlegume harvests: Establish a realistic end for harvest output, and from this end gauge the sum of N that the harvest must roll up. Estimate the sum of N that will be supplied by the mineralization of dirt organic N and harvest residues. Use any available manure N to supplement the dirt and harvest residue supplies. If necessary, supplement these nitrogen beginnings with adequate fertiliser to run into the output end for the peculiar harvest. Apply any needful fertiliser merely before the period of most rapid harvest consumption to minimise leaching and denitrification. These stairss are to the full described in the Cornell Field Crops and Soils Handbook, the 1990 Cornell Recommends for Field Crops, and two fact sheets by Klausner and Bouldin ( see # 8220 ; For Further Reading # 8221 ; for mention information ) . One method of increasing the efficiency of fertiliser usage and diminishing the sum lost to groundwater is to detain a part of the nitrogen application until the harvest is turning instead than using it all at the clip of seting ( fig. 2. See fact sheet ) . Field experiments have shown that dividing fertiliser applications can increase the efficiency of N usage, maintain harvest outputs, and lessening fertiliser costs. Another technique for run intoing harvest demands while diminishing leaching losingss is to provide N in an organic signifier such as manure or leguminous plant residues. Because organic N is bit by bit converted into inorganic N, merely little sums are in a soluble signifier susceptible to leaching at any one clip. It is estimated that the sum of atmospheric N taken up by leguminous plants approximately equals the sum removed by reaping. If harvested hay is removed from the farm, so dirt N should stay about changeless. If the hay is fed to animate beings on the farm, about one-half of the N can be returned to the Fieldss if the manure is handled carefully. To avoid inordinate N losingss through volatilization, overflow, and leaching, follow these processs in managing manures: Collect manure every bit shortly as possible after it is deposited, and conserve the liquid part. Shop manure under conditions that prevent drying or drainage Apply manure to the field near to the clip of planting, so that the available N will be taken up by workss instead than leached, lost to the ambiance, or converted to organic signifiers. Plow manure under every bit shortly as possible after distributing to minimise ammonia volatilization. ( See the two fact sheets by Klausner and Bouldin for more information on manure direction. ) Decisions Nitrogen is likely to be in short supply for harvest production unless supplemented by legume harvest residues or by the application of fertilisers, manures, or other high-nitrogen stuffs. Nitrogen repairing microbes replenish dirt N by change overing the comparatively inert N of the ambiance into a signifier that can be used by populating beings. Since biological arrested development of N is non normally sufficient to run into the demands of intensive harvest production, nevertheless, extra beginnings may be needed. Fertilization strategies should be designed to run into harvest N needs without losing inordinate sums of N to groundwater. This is accomplished by gauging N demands and run intoing these demands every bit much as possible with manure or other organic beginnings. The greatest potency for nitrate leaching occurs if fertiliser is applied at a clip when no harvests are turning, such as during spring planting or in the autumn after crop. Leaching losingss can be reduced by using N in increases during the periods of rapid works growing. Using manure or slow- release fertilisers besides limits leaching.losses because plant-available ( and leachable ) N is supplied bit by bit instead than all at one time. Even with these beginnings, nevertheless, leaching can happen if the N supplied exceeds the ability of the harvest to utilize it. Turning leguminous plants and utilizing organic dirt amendments enrich the dirt with organic N, which does non leach and provides a uninterrupted supply of plant- available N as it slowly decomposes. Adding organic affair to dirty provides extra benefits by heightening the dirt # 8217 ; s ability to retain H2O and dissolved foods in the root zone where they are available to workss. Protecting organic surface soils from eroding, supplying organic dirt amendments, and pull offing H2O and fertiliser applications for upper limit works consumption will take to efficient fertiliser usage and protection of groundwater quality. Basic Information Name: Nitrogen Symbol: N Atomic Number: 7 Atomic Mass: 14.00674 amu Melting Point: -209.9? C ( 63.250008? K, -345.81998? F ) Boiling Point: -195.8? C ( 77.35? K, -320.44? F ) Number of Protons/Electrons: 7 Number of Neutrons: 7 Categorization: Non-metal Crystal Structure: Hexangular Density @ 293 K: 1.2506 g/cm3 Color: colorless Facts Date of Discovery: 1772 Inventor: Daniel Rutherford Name Origin: Grecian Uses: signifiers most of atmosphere Obtained From: from liquid air Description Nitrogen is a Group 15 component. Nitrogen makes up approximately 78 % of the ambiance by volume. The ambiance of Mars contains less than 3 % N. Nitrogen can be obtained by liquefaction and fractional distillment from air. The component seemed so inert that Lavoisier named it azote, intending # 8220 ; without life # 8221 ; . However, its compounds are critical constituents of nutrients, fertilisers, and explosives. Nitrogen gas is colorless, odorless, and by and large inert. As a liquid it is besides colorless and odorless, and is similar in visual aspect to H2O. When N is heated, it combines straight with Mg, Li, or Ca. When assorted with O and subjected to electric flickers, it forms azotic oxide ( NO ) and so the dioxide ( NO2 ) . When heated under force per unit area with H in the presence of a suited accelerator, ammonium hydroxide signifiers ( Haber procedure ) . Nitrogen is # 8220 ; fixed # 8221 ; from the ambiance by bacteriums in the roots of certain workss such as trefoil. Hence the utility of trefoil in harvest rotary motion. General information Inventor: Daniel Rutherford Date discovered: 1772 Discovered at: Scotland Meaning of name: From the Greek words # 8220 ; nitron cistrons # 8221 ; intending # 8220 ; nitre # 8221 ; and # 8220 ; organizing # 8221 ; and the Latin word # 8220 ; nitrum # 8221 ; ( nitre is a common name for K nitrate, KNO # ) Physical informations Standard province: gas at 298 K Color: colorless Density of solid at ambient temperature/kg m-3: no informations Molar volume/cm3: 13.54 Temperatures ( /K ) runing point: 63.05 boiling point: 77.36 I. Introduction Nitrogen, symbol N, gaseous component that makes up the largest part of the Earth # 8217 ; s atmosphere. The atomic figure of N is 7. Nitrogen is in group 15 ( or Va ) of the periodic table Nitrogen was isolated by the British doctor Daniel Rutherford in 1772 and recognized as an elemental gas by the Gallic chemist Antoine Laurent Lavoisier about 1776. II. Properties Nitrogen is a colorless, odorless, tasteless, atoxic gas. It can be condensed into a colorless liquid, which can in bend be compressed into a colorless, crystalline solid. Nitrogen exists in two natural isotopic signifiers, and four radioactive isotopes have been unnaturally prepared. Nitrogen thaws at -210.01? C ( -346.02? F ) , boils at -195.79? C ( -320.42? F ) , and has a denseness of 1.251 g/liter at 0? C ( 32? F ) and 1 atmosphere force per unit area. The atomic weight of N is 14.007. Nitrogen is obtained from the ambiance by go throughing air over heated Cu or Fe. The O is removed from the air, go forthing N asso rted with inert gases. Pure N is obtained by fractional distillment of liquid air ; because liquid N has a lower boiling point than liquid O, the N distills off first and can be collected. Nitrogen composes about four-fifths ( 78.03 per centum ) by volume of the ambiance. Nitrogen is inert and serves as a dilutant for O in combustion and respiration procedures. It is an of import component in works nutrition ; certain bacteriums in the dirt convert atmospheric N into a signifier, such as nitrate, that can be absorbed by workss, a procedure called nitrogen arrested development. Nitrogen in the signifier of protein is an of import component of carnal tissue. The component occurs in the combined province in minerals, of which potassium nitrate ( KNO3 ) and Chile potassium nitrate ( NaNO3 ) are commercially of import merchandises. Nitrogen combines with other elements merely at really high temperatures or force per unit areas. It is converted to an active signifier by go throughing thro ugh an electric discharge at low force per unit area. The N so produced is really active, uniting with alkali metals to organize azides ; with the vapour of Zn, quicksilver Cd, and arsenic to organize nitrides ; and with many hydrocarbons to organize hydrocyanic acid and nitriles, besides known as cyanides. Activated N returns to ordinary N in about one minute. In the combined province N takes portion in many reactions ; it forms so many compounds that a systematic strategy of compounds incorporating N in topographic point of O was created by the American chemist Edward Franklin. In compounds nitrogen exists in all the valency provinces between -3 and +5. Ammonia, hydrazine, and hydroxylamine represent compounds in which the valency of N is -3, -2, and -1, severally. Oxides of nitrogen represent N in all the positive valency provinces. III. Uses Most of the N used in the chemical industry is obtained by the fractional distillment of liquid air. It is so used to synthesise ammonium hydroxide. From ammonium hydroxide produced in this mode, a broad assortment of of import chemical merchandises are prepared, including fertilisers, azotic acid, urea, hydrazine, and aminoalkanes. In add-on, an ammonium hydroxide compound is used in the readying of azotic oxide ( N2O ) a colorless gas popularly known as express joying gas. Assorted with O, azotic oxide is used as an anaesthetic for some types of surgery. Used as a coolant, liquid N has found widespread application in the field of cryogenies. With the recent coming of ceramic stuffs that become superconductive at the boiling point of N, the usage of N as a coolant is increasing ( see Superconductivity ) .