Criticality and Condensation in a Non-Conserving Zero Range Process

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环境政策分析,英文版(练习翻译)

环境政策分析,英文版(练习翻译)

123 Array 4567891011111121314151617181920111212223242526272829301113132333435363738394011171should not automatically bar adoption of measures to prohibit or otherwise regulate the activity, and, in stronger versions, further asserts that uncertainty provides an affirmative justification for regulating an activity or regulating it more stringently than in the absence of uncertainty. Strong versions of PP hold that regulators should adopt “worst case” presumptions regarding the harms of activities posing an uncertain potential for significant harm; should prohibit such activities or require them to adopt best available technology measures;that regulatory costs should be disregarded or downplayed in such decisions;and that the proponents of such activities should bear the burden of establishing their safety in order to avoid such regulatory controls. The article also considers the relevance for regulatory decisions of uncertainties regarding the costs of regulating an activity as well as uncertainties regarding harms. It further considers the implications of the circumstance that regulatory decisions about a given environmental issue may be made sequentially over time and benefit from additional information developed in the interim between earlier and later decisions. The essay concludes that, while preventive regulation of uncertain risks is often appropriate and should incorporate precautionary elements where warranted by consideration of risk aversion or information acquisition, strong versions of PP do not provide a conceptually sound or socially desirable prescription for regulation.I. INTRODUCTION: ENVIRONMENTAL DECISION MAKING UNDER UNCERTAINTY AND THE PRECAUTIONARY PRINCIPLE The following are examples of regulatory decisions involving uncertain risks. In each case, consider whether a regulator should permit the potentially harmful activity to commence or continue, or, alternatively, to prohibit or otherwise regulate it, and the implications of sequential regulatory decision making and the opportunity to develop additional information to reduce uncertainties regarding the risks of harms posed by an activity and/or the costs of regulation.•Whether to prohibit the sale of meat products from cattle that have received bovine growth hormone injections.•Whether to prohibit the construction of an astronomic observatory atop Mt.G raham, in New Mexico, the only known habitat of the Mt. G raham Red Squirrel, a subspecies of the western red squirrel located only on Mt. Graham;other subspecies of the red squirrel are abundant in the Western United States.72RICHARD B. STEWART12345678910111111213141516171819201112122232425262728293011131323334353637383940111•Whether to prohibit field releases of crop plants that have been genetically modified using DNA technologies.•Whether to adopt a National Ambient Air Quality Standard (NAAQS) to limit short-term (10-minute) exposures to elevated levels of sulfur dioxide (SO 2). Several laboratory studies indicate that asthmatics exposed to higher short-term SO 2exposures experience temporary airway resistance that makes breathing more difficult.•Whether to prohibit introduction of sucralose, an artificial beverage sweetener that has been touted as safer than saccharin or aspartame, the artificial sweeteners currently in use.•Whether to prohibit the dumping of wastes of any sort at sea.•Whether to develop defenses against collisions with the earth by asteroids and other near-earth objects.•Whether to eliminate the use of chlorine to treat drinking water.•Whether to prohibit the use of glyphosate (“Roundup”), a broad-spectrum non-selective herbicide that is harmless to animals.•Whether to prohibit or tightly regulate the conversion of rainforest to agricultural or other uses.•Whether to immediately initiate strict limits on greenhouse gas emissions in order to limit the potential adverse effects of climate changes attributable to such emissions.In evaluating these and other environmental regulatory decision-making issues,the extent of available knowledge regarding environmental harm that may be caused by the activity in question can be conceptually classified in three ideal type categories:Type 1. The harm that the activity will cause is known and determinate. If,for example, the Mt. Graham observatory is built, the Mt. Graham red squirrel population will be wiped out within 20 years.Type 2. The harm is probabilistic in character but its probability distribution is known. For example, if the observatory is built, there is a 40% probability that the squirrel population will be wiped out within 20 years and a 60% probability that it will survive another 1000 years, at which point it will become extinct from natural “background” causes. In this situation we deal with a risk of harm, but the risk (comprising both the probability of an adverse effect occurring and the magnitude of the adverse effect if it occurs) is determinate.Type 3. There is a risk of harm that is uncertain. Thus, the probability of harm occurring, and/or the magnitude of the harm if it occurs, is not determi-nate and is subject to substantial uncertainty. To take the Mt. Graham example,Environment al Regulat ory Decision Making Under Uncert aint y 737312345678910111111213141516171819201112122232425262728293011131323334353637383940111it may be uncertain, based on current knowledge, whether any adverse effect on the squirrels will occur. If any adverse effect does occur, its magnitude is uncertain. Thus, it may be uncertain what percentage of the population may be lost, whether any given level of loss will result in extinction of the subspecies,and when possible losses or extinction may occur. There may also be cases where the type of harm, if any, that may occur is not known.The difference between Type 2 cases and Type 3 cases is obviously one of degree, but the distinction between the two ideal types is very useful for purposes of analysis. Very many environmental problems are Type 3 cases,characterized by uncertainty regarding risks of harm, although the nature and degree of uncertainty varies widely from case to case. These uncertainties have many potential causes, including lack of data, limitations in scientific understanding of causal relationships, medical and ecosystem complexity, and “trans scientific” gaps in the capacities of science.1There may also be substantial uncertainties regarding the costs of prohibiting or otherwise regulating the activity in question. In many situations, such uncertainties can be reduced by the development of additional information and knowledge as discussed further below.The common law traditionally awards damages only ex post for harm that has occurred and has been shown to have been caused by another’s activity. It grants injunctive relief ex ant e only if an activity poses an imminent and substantial likelihood of serious irreparable harm. Many environmental risks of types 2 and 3 would not qualify for an award of damages or prophylactic relief under this standard. In theory, ex post liability for harm caused could provide the requisite incentives for actors to manage their activities so as to prevent excessive risks of harm appropriately. In practice, however, these incentives have for a variety of reasons proven inadequate to prevent excessive environ-mental harm from occurring.2Accordingly, administrative programs of preventive ex an t e regulation have been widely adopted in the United States and other countries to regulate activities that pose substantial risks of environmental harm, even in cases where it is not certain that harm will actually occur. International agreements, such as the Vienna Convention for the Protection of the Ozone Layer and the Framework Convention on Climate Change, have also been adopted to address such risks.Preventive regulatory programs have been adopted not only in cases where activities have been shown to cause harm, but also in cases involving risks of harm, including cases of substantial uncertainty in the risk of harm.3Quantitative risk analysis and cost-benefit analysis are increasingly being used in connection with the preventive approach to regulation.4Under many preventive regulatory74RICHARD B. STEWART12345678910111111213141516171819201112122232425262728293011131323334353637383940111programs, regulators have the burden of establishing a significant risk of harm before imposing regulatory controls,5although under some programs, such as U.S. FDA new drug and food additive approvals and EPA registration of pesticides, the applicant bears the burden of showing product safety.In recent years, environmental advocates and many environmental law scholars, particularly in the field of international environmental law, have argued that environmental regulatory decisions and policies should follow a precautionary principle (PP).6The focus of PP is on appropriate regulatory policy in Type 3 cases where the risks of harm posed by an activity are characterized by substantial uncertainty. PP advocates argue for a precautionary approach to regulation in the face of such uncertainty. They often criticize prevailing preventive approaches to regulation on the grounds that they place the burden on regulators to show that an activity will cause serious harm or poses a high probability of serious harm before regulatory controls may be adopted. They argue that, given the lack of scientific capacities to predict which activities will cause serious or irreversible harms, this approach results in seriously inadequate environmental protection. They often also contend that existing preventive regulatory approaches give undue weight to costs in establishing controls.7Various versions of PP, mostly weak ones, have been incorporated or invoked in a number of recent international environmental declarations and conventions,including the Framework Convention on Climate Change 8and the EU Maastricht treaty.9These documents and the writings of PP advocates and of academics provide widely varying formulations of PP. It has been claimed that PP is already, or is becoming established as a binding principle of customary international law.10PP skeptics and critics, however, have contended that the heterogeneity of PP formulations, many of which are quite vague and indeterminate, demonstrates that that there is no single or determinate PP.11Thus, they have concluded that the precautionary principle is a “composite of several value-laden notions and loose, qualitative descriptions” and that accordingly its “operational usefulness ... is doubtful.”12They also deny that PP has been established as customary international law.13Criticisms of PP as indeterminate and conceptually fuzzy have merit. With a very few exceptions, there is a remarkable lack of analytic care or rigor regarding the substance of, and justification for, various versions of PP by those who advocate or favor their adoption. One can, however, identify four different PP conceptions that have emerged in legal instruments, international and national governmental declarations, advocacy statements, and the academic liter-ature that can serve as a useful basis for analysis and evaluation. These four versions of PP are as follows:Environment al Regulat ory Decision Making Under Uncert aint y 757512345678910111111213141516171819201112122232425262728293011131323334353637383940111PP1. Scientific uncertainty should not automatically preclude regulation of activities that pose a potential risk of significant harm (Non-Preclusion PP).PP2. Regulatory controls should incorporate a margin of safety; activities should be limited below the level at which no adverse effect has been observed or predicted (Margin of Safety PP).PP3. Activities that present an uncertain potential for significant harm should be subject to best technology available requirements to minimize the risk of harm unless the proponent of the activity shows that they present no appreciable risk of harm (BAT PP).14PP4. Activities that present an uncertain potential for significant harm should be prohibited unless the proponent of the activity shows that it presents no appreciable risk of harm (Prohibitory PP).What unites these different formulations is a focus on uncertainty regarding risks as the key factor guiding regulatory decisions. Some discussions of the PP blur the distinction between known (Type 2) and uncertain risks (Type 3),but the most careful commentators make clear that the precautionary principle is addressed to uncertain risks (Type 3) as such.15PP1 and PP2 are weak versions of precautionary approaches. Unlike the strong versions, PP3 and PP4, they do not mandate regulatory action and do not make uncertainty regarding risks an affirmative justification for such regulation.Thus, PP1 is negative in character; it states that uncertainty should not preclude regulation but does not provide affirmative guidance as to when regulatory controls should be adopted or what form they should take. This is the approach that is most widely invoked in international treaties and declarations. While the exact wording may vary, this principle of non-preclusion always sets up a threshold, e.g. an uncertain risk of serious damage,and then makes the negative prescription that, once that threshold has been triggered, regulators cannot rely on this fact alone to deny regulation. For example, the Bergen Ministerial Declaration states: “Where there are threats of serious or irreversible damage, lack of full scientific certainty should not be used as a reason for postponing measures to prevent environmental degradation.”16The Cartagena Protocol goes further by clarifying that uncertainty can not, in and of itself, justify the decision not to regulate, nor,presumably, the alternative decision to impose regulation:Lack of scientific certainty due to insufficient relevant scientific information and knowledge regarding the extent of the potential adverse effects of a living modified organism shall not prevent [a] Party from taking a decision, as appropriate. Lack of scientific knowledge or scientific consensus should not necessarily be interpreted as indicating a particular level ofrisk, an absence of risk, or an acceptable risk.1776RICHARD B. STEWART12345678910111111213141516171819201112122232425262728293011131323334353637383940111This principle of non-preclusion rejects the common law position that harm must be shown to have occurred or be imminent before legal liabilities or controls may be imposed. It also rejects the position, often asserted by industry,that significant uncertainty about risks should preclude imposition of preven-tive regulatory controls. Of all the formulations of the PP, this approach is the most often invoked and is most likely to be recognized as a part of customary international law; it is already widely accepted that a preventive approach, under which regulatory controls are adopted to prevent or reduce risks of harm even though the magnitude or even the occurrence of harm is uncertain, is justified in at least some circumstances.18Yet, the very generality and lack of specific prescriptions of PP1 may preclude it from being recognized as a binding norm.19PP2 likewise fails to specify when or what form of regulation should be adopted, but instructs that, whenever regulation is adopted, it should incorporate a margin of safety. Unlike PP1, PP2 is operative only after regulators have made the determination to regulate. Once this decision is made,regulators must first determine the maximum “safe” level of an activity, and then only allow the activity at some degree lower than that level (the “margin of safety”). This is a common approach in U.S. environmental law. An example is the Sustainable Fisheries Act of 1996, in which the optimum allowable yield from a fishery “is prescribed on the basis of the maximum sustainable yield from the fishery, as reduced by” relevant factors including “ecological” factors.20PP2 is consistent with (although it does not necessarily mandate) many commen-tators’ views that PP requires that regulators allow “large margins for error” in risk assessments.21It represents one formulation of the PP premise that: “Given scientific ignorance, prudent pessimism should be favoured over hazardous optimism.”22PP2 is not explicitly set forth in any international agreements and declarations, but its approach is implicit in some international agreements that require or provide for the adoption of precautionary measures.23The weak versions of the PP are fully compatible with and are often reflected in many well-established preventative regulatory programs that have been adopted at the domestic level by many countries and by international agreement over the past 30 years. These programs often authorize prophylactic regulation of uncertain risks in appropriate circumstances even in the absence of a showing that harm will actually occur. In many cases, they explicitly require a margin of safety in setting regulatory standards.24Thus the weak versions of PP do not represent or justify any basic change in the preventive approach to regulation that has generally prevailed over the past 30 years. They accordingly provide no basis for arguing that existing preventive regulatory programs are not sufficiently “precautionary” and need to be fundamentally changed in order to reflect precautionary principles.Environment al Regulat ory Decision Making Under Uncert aint y 777712345678910111111213141516171819201112122232425262728293011131323334353637383940111There are, however, important differences between established programs of preventive regulation and the strong versions of PP. Weak precautionary programs generally do not make the existence of uncertainty regarding risks as such a mandatory or distinct basis for imposing regulatory controls. PP3 and PP4, on the other hand, require regulators to regulate, or regulate more stringently, activities that pose risks that are more uncertain relative to risks that are less uncertain, and thus represent a significant change in regulatory concept and result.Under PP3, when regulators determine that there is a serious but uncertain risk, they must impose BAT measures. For example, the Second International Conference on the Protection of the North Sea calls for parties to:[R]educ[e] polluting emissions of substances that are persistent, toxic and liable to bio-accumulate at source by the use of the best available technology and other appropriate measures. This applies especially when there is reason to assume that certain damage or harmful effects on the living resources of the sea are likely to be caused by such substances,even where there is no scientific evidence to prove a causal link between emissions and effects (“the principle of precautionary action”).25Such a prescription does not appear to allow regulators to decide what sort of regulation is required, including no regulation: if there is an uncertain risk of serious harm, BAT measures should be imposed. However, some flexibility may remain under PP3 since the intensity of BAT controls may vary depending on the magnitude of the potential risk relative to the costs of controls, in accor-dance with a principle of proportionality.26PP4 imposes an even more stringent prescription upon regulators. Under this formulation, if there is an uncertain but serious risk of harm, the activity in question should not be undertaken at all until it is proven to be safe by the proponent of the activity. Thus, the Final Declaration of the First European “Seas at Risk” Conference provides that:The “burden of proof” is shifted from the regulator to the person or persons responsible for the potentially harmful activity, who will now have to demonstrate that their actions are not/will not cause harm to the environment. If the “worst case scenario” for a certain activity is serious enough, then even a small amount of doubt as to safety of that activity is sufficient to stop it taking place.27While this version of the PP presumably allows regulators some latitude to determine how serious an uncertain risk must be to invite regulation, it requires prohibition of the activity once the relevant risk threshold is met.The strong versions of PP, PP3 and PP4, are the focus of this essay.Accordingly, unqualified references to PP in the following discussion should be understood as referring to the strong versions of PP. Unlike the weak versions 78RICHARD B. STEWART12345678910111111213141516171819201112122232425262728293011131323334353637383940111of PP and the preventive approach to regulation generally, they make the existence of uncertain risks of significant harm both a sufficient and mandatory basis for imposing regulatory controls. We may term this the “uncertainty-based potential for harm” prescription for regulation. Different PP formulations incorporating this precept vary in the criteria for determining the potential for harm threshold that triggers the requirement of regulation, including how great the probability of harm must be, its character, and its magnitude. Some formulations, for example, stress that the probability of harm must be substan-tial and the harm that may eventuate must be “serious and irreversible.”28Other formulations enunciate less demanding criteria.29In some strong PP formula-tions, once the applicable risk threshold is met, regulation is mandatory;regulatory compliance costs, including the social costs involved in forgoing the benefits of activities subject to regulatory prohibition or restriction, are not included as a factor to be considered in the regulatory decision.30Some formu-lations explicitly allow for consideration of costs, but relegate them to a distinctly secondary role, while others introduce the principle of proportion-ality, tailoring the extent and character of the regulatory response adopted to the gravity of the risk in question.31Under PP3, for example, the costs of BAT controls might be taken into account in determining whether a given technology is “available.” It might be concluded that very costly technology controls are not as a practical matter “available.” Under PP4, in cases where potential risks are judged less serious or where the social benefits of the activity are high,prohibitory controls might be adopted for only a limited initial period subject to “sunset” provisions or reconsideration, or field trials may be permitted.32Strong versions of the PP also often hold that the burden of resolving uncertainty should be borne by the proponent of an activity rather than by regulators or opponents of the activity.33Accordingly, in order to avoid or lift regulatory prohibitions or BAT requirements, the proponent of an activity bears the burden of demonstrating that it does not present a potential for significant harm. Proponents of regulation, however, bear some initial threshold burden of production and persuasion. They must establish that an activity poses risks (albeit uncertain) of harm, including a potential for significant harm. Once that threshold burden is satisfied, however, the burden shifts to the activity proponent to resolve the uncertainty and show that that it does not have a potential for significant harm.34The normative core of the strong versions of PP, which distinguishes PP-based regulation from preventive regulation generally, is the principle that uncertainty regarding risks is an affirmative justification for adopting regulatory controls or adopting more stringent controls than would be appropriate in the case of activities posing more determinate risks. In the face of uncertainties regardingEnvironment al Regulat ory Decision Making Under Uncert aint y 797912345678910111111213141516171819201112122232425262728293011131323334353637383940111risk, PP holds that decision makers should err on the side of precaution and envi-ronmental protection and, in effect, make “worst case” presumptions about the probability and magnitude of harm that an activity poses; precisely how “worst case” is defined (“reasonable worst case,” etc.) varies in different PP formula-tions.35The justifications advanced by PP proponents for adopting its prescrip-tions center around limitations in our ability to predict which activities will cause serious, irreversible environmental harms.36The predictive capacity of science is limited. For example, science has often been unable to predict, in a sufficiently timely fashion to support effective preventive action, the occurrence of serious environmental harms such as asbestosis, stratospheric ozone depletion, or the ecological harms caused by DDT. Thus, a regulatory policy that requires regulators to demonstrate that an activity causes harm or even a significant risk of harm before imposing controls will result in the occurrence of serious environmental harms. Some of these harms, such as biodiversity loss or highly disruptive changes in natural systems resulting from rapid global warming, may be irreversible and seriously harm future generations. Accordingly, decision makers should err on the side of pre-caution and protection of the planet by adopting PP-based regulatory controls on activities involving uncertain risks that pose a potential for significant harm.The PP literature provides little in the way of helpful guidance on what regulators must show in order to establish a potential for harm that triggers PP.37While some PP proponents appear to assume that nature is inherently vulnerable and precarious rather than resilient, such a general presumption is not sufficient to show that a given activity triggers PP. The bovine growth hormone dispute suggests that a showing that a substance similar in chemical structure to the substance in question can cause harm may be sufficient.38The BtCorn-Monarch butterfly controversy suggests that a report of a single experimental study, albeit one quite unrepresentative of field conditions, can be enough to trigger PP controls if it is sufficiently widely publicized.39Under strong versions of PP, once the risk posed by an activity satisfies the threshold that triggers a worst case presumption, regulators must then follow a set of relatively stringent regulatory prescriptions. They must prohibit or impose BAT requirements on the activity; shift the burden to the activity proponent to show that the activity is “safe” in order to avoid or lift these regulatory require-ments; and disregard or downplay regulatory costs in implementing regulatory requirements. Thus, PP can be analyzed as containing two basic components:First, a worst case presumption for uncertain risks that meet a triggering threshold. Second, a set of regulatory decision rules that are mandatory once the presumption is triggered. These components can be analyzed separately.80RICHARD B. STEWART12345678910111111213141516171819201112122232425262728293011131323334353637383940111。

关于质疑批判能力的作文

关于质疑批判能力的作文

关于质疑批判能力的作文英文回答:Questioning criticality is a crucial element of effective intellectual inquiry and personal growth. It involves actively examining the assumptions, evidence, and conclusions of any given perspective, regardless of its source. Individuals with strong critical thinking skills can identify biases, evaluate the strength of arguments, and form well-informed judgments. This ability is essential in all aspects of life, from making personal decisions to engaging in public discourse.Several key strategies can enhance critical thinking skills. Firstly, it is important to be aware of one's own biases and assumptions. This self-awareness allows individuals to recognize how their personal experiences and perspectives may shape their interpretation of information. Secondly, actively seeking out diverse viewpoints and perspectives can help challenge preconceived notions andbroaden one's understanding. Engaging in respectfuldialogue with individuals who hold different opinionsfosters critical thinking and promotes mutual learning.Furthermore, carefully evaluating the evidencepresented in support of an argument is vital. This involves examining the quality, relevance, and sufficiency of the evidence. Critically assessing the strength of arguments requires identifying logical fallacies and examining the validity of inferences. It is also essential to consider alternative explanations and counterevidence to ensure a comprehensive understanding of the issue.Critical thinking is an ongoing process that requires practice and dedication. By actively questioning assumptions, seeking diverse perspectives, and evaluating evidence, individuals can develop their ability to think critically and make informed judgments. This skill is essential for navigating an increasingly complex and interconnected world, where critical evaluation is vitalfor making wise choices and engaging in productive dialogue.中文回答:提出质疑批判能力是一项至关重要的任务,对于有效的智力探究和个人成长来说至关重要。

The Significance of Critical Thinking

 The Significance of Critical Thinking

Critical thinking is an essential skill that allows individuals to analyze, evaluate, and interpret information and ideas in order to make informed decisions and solve problems effectively. It involves the ability to think logically, rationally, and objectively, while considering multiple perspectives and being open to new ideas.The significance of critical thinking cannot be overstated, as it plays a crucial role in various aspects of life, including education, work, and everyday decision-making. In the context of education, critical thinking is vital for students to develop a deep understanding of the subjects they are studying. It enables them to question, challenge, and evaluate the information they are being presented with, rather than simply accepting it at face value. This not only leads to a more meaningful and comprehensive learning experience but also equips students with the skills they need to become independent and lifelong learners.In the workplace, critical thinking is highly valued by employers as it allows individuals to make well-reasoned decisions, solve complex problems, and innovate. Employees who possess strong critical thinking skills are able to gather and analyze relevant information, identify patterns and trends, and make sound judgments based on evidence and logic. This is particularly important in today's fast-paced and competitive business environment, where the ability to adapt to change and think creatively is essential for success.Furthermore, critical thinking is essential for individuals to become responsible and informed citizens. In a world where information is readilyavailable and often conflicting, the ability to critically evaluate and discern the credibility of sources is crucial. It allows people to make informed decisions about political, social, and ethical issues, and to engage in constructive and well-informed discussions and debates.Moreover, critical thinking is closely related to problem-solving skills. By approaching problems and challenges with a critical mindset, individuals are able to break down complex issues into manageable parts, identify the root causes, and develop effective solutions. This not only leads to more efficient problem-solving but also encourages innovation and creativity.In addition, critical thinking fosters intellectual humility and open-mindedness, as individuals learn to consider and appreciate different perspectives and ideas. It also encourages intellectual independence and self-reflection, as people are encouraged to question their own assumptions and beliefs, and to consider alternative viewpoints.Finally, critical thinking is essential for personal growth and development. By honing this skill, individuals are better equipped to make informed decisions about their lives, relationships, and personal goals. They are able to weigh the pros and cons of different options, anticipate the potential consequences of their actions, and make choices that align with their values and aspirations.In conclusion, critical thinking is of paramount significance in various aspects of life. It empowers individuals to become active and responsible learners, effective problem-solvers, informed citizens, and thoughtful decision-makers. By fostering this skill, we can cultivate a society of independent and analytical thinkers who are able to navigate the complexities of the modern world with confidence and competence.。

核电专业词汇

核电专业词汇

A阿伏伽德罗数Avogadro number安全保护回路safety loop安全保护通道safety channel安全保健水平safe health level安全报警系统safe alarm system安全部件safety component安全程序safety procedure安全出口safe escape安全导则safety guides安全动作系统safety actuation system安全端safe end安全法规safe regulation安全分隔准则safe separation criterion 安全分级safety classification安全分析safety analysis安全分析报告safety analysis report安全封存safe enclosure安全隔离阀safety isolating valve安全管理security control安全剂量safe dose安全剂量safety dose安全间距safe spacing安全监测器safety monitor安全监督safety supervision安全检查safety inspection安全壳containing vessel安全壳containment vessel安全壳测量仪表containment instrumentation安全壳厂房containment building安全壳吹扫系统containment purge system安全壳地坑containment sump安全壳钢衬containment steel liner安全壳隔离containment isolation安全壳隔离系统containment isolation system安全壳贯穿件containment penetration 安全壳贯穿件containment shell penetration安全壳环形空间containment annulus安全壳结构containment structure安全壳金属包层containment metal enclosure安全壳空气清洁系统containment air cleaning system安全壳冷却系统containment cooling system安全壳密封性containment leaktightness 安全壳内吊车containment crane安全壳排热系统containment heat removal system安全壳喷淋系统containment spray system安全壳屏蔽containment barrier安全壳疏水系统containment drain system安全壳完整性containment integrity安全壳消压系统containment pressure suppression system安全壳淹没系统containment deluge system安全控制safety control安全联锁safety interlock安全浓度safe concentration安全评价safety assessment安全评价报告safety evaluation report安全设施safe gear安全设施safeguard安全条例safety regulations安全停堆safe shutdown安全停堆地震safe shutdown earthquake 安全停堆系统safety shutdown system安全系统辅助设施safety system support features安全限值safety limit安全相关事件safety-related incident安全性能safety performance安全裕度safety margin安全原理safety philosophy安全运行safe operation安全直径safe diameter安全重要部件component important to safety安全重要物项items important to safety 安全注入系统safety injection system安全准则safety criterion安全走廊safe corridor安装开口construction openingB钯palladium白边界white boundary白反射white reflection白交界面white interface白血病leucemia白噪声white noise百年一遇洪水hundred year flood颁发安全许可证grant of safety licenses 半剂量辐射half irradiation半球顶hemispherical dome半数致死剂量half-lethal dose半数致死剂量median lethal dose半数致死时间median lethal time半衰期half-life半速汽轮机half speed turbine半周期half cycle伴随中子通量adjoint flux伴随中子通量密度adjoint of the neutron flux density棒插入rod insertion棒行程rod stroke包覆材料coating material包覆层coating layer包覆颗粒燃料coated particle fuel包覆颗粒芯核particle kernel包壳capsule包壳cladding包壳jacket包壳壁厚can thickness包壳材料canning material包壳材料cladding material包壳脆化cladding embrittlement包壳导热率conductivity of cladding包壳工艺cladding process包壳鼓胀cladding ballooning包壳管cladding tube包壳管壁厚clad tube wall thickness包壳管材料clad tube material包壳管破裂clad tube rupture包壳管损坏clad damage包壳管温度系统clad tube temperature coefficient包壳膨胀clad expansion包壳破裂can burst包壳破裂can rupture包壳破裂cladding bursting包壳破裂率clad failure rate包壳破损can failure包壳缺陷can defect包壳缺陷cladding defect包壳熔化can meltdown包壳熔化clad meltdown包壳蠕变cladding creep包壳坍塌cladding collapse包壳完整性clad integrity包壳完整性cladding integrity包壳温度cladding temperature包壳-芯块间隙can-pellet clearance包装物监测仪package monitor饱和度degree of saturation饱和蒸汽发生器saturated steam generator饱和蒸汽供应管线saturated steam supply line饱和蒸汽汽轮机saturated steam turbine 保健监督health surveillance保健物理监测health physics monitoring 保健物理研究堆health physics research reactor保卫区security area保卫系统security system保险费premium保障措施safeguard measures保障技术safeguards technique保障制度safeguard system保证guarantee保证出力firm capacity保证期guaranty period保证输出功率guaranteed output报关单customs clearance报价日offering date报价书offer letter报价有效期offering period报警alert报警光字牌alarm window报警及重置alarm and setback报警剂量计alarm dosimeter报警信号alarm signal备用安全系统back-up safety system备用泵backing pump备用过滤器back-up filter备用冷却剂系统backup coolant system 备用停堆系统complementary shutdown system备用停堆系统reserve shutdown system 倍增中子multiplication neutrons本底测量background survey本底等效放射性background equivalent activity本底放射性水平background activity level本底积累background buildup本底计数background count本底剂量background dose本底监测background monitoring本底截面background cross-section本底凝聚background condensation本底水平background level本底噪声background noise本底照射background exposure本底中子background neutron逼近临界approach to criticality逼近临界状态approach to criticality phase比活度specific activity比千瓦负荷kilowatt rating比燃耗specific burn-up比色剂量计colorimetric dosimeter闭环closed cycle闭环反应堆系统closed cycle reactor system闭式冷却系统closed cooling system闭式通道closed channel壁厚变化wall thickness transition避雷器arrester边界boundary边界条件boundary conditions边界效应boundary effect扁平堆pancake reactor 扁平堆芯pancaked core变频机组frequency converter set变性的denatured变性燃料denatured fuel标定管calibrating tube标定曲线calibration curve标签label标准安全分析报告standard safety analysis report标准放射源standard radioactive source 标准燃料棒standard fuel rod标准响应谱standard response spectrum 标准源standard source标准中子源standard neutron source表面活度surface activity表面活化剂active surface agent表面冷却堆surface-cooled reactor表面污染控制水平control level of surface contamination表面吸收剂量surface absorbed dose表面硬化hard facing表面沾污监测surface monitoring波纹dimple补偿贸易countertrade补给水平衡balance of makeup water不安全燃料unsafe fuel不符合discrepancy不符合non-conformance不符合报告non-conformance report不工作状态off position不活动断层inactive fault不间断电源uninterruptible power supply不可进入的反应堆厂房inaccessible reactor building不可进入区inaccessible area不可抗力force majeure不可信事件incredible events不可预见费accidental cost不可预见费contingency allowance不扩散核武器条约Non-Proliferation Treaty不停堆换料on-line refuelling不停堆换料on-load fuelling不停堆换料堆on-load refuelled reactor 不停堆加料on-line loading不停堆维修on-line maintenance不停堆维修on-load maintenance不透气的air proof不稳定性instability不相干辐射incoherent radiation不相干散射incoherent scattering不泄漏概率non-leakage probability钚plutonium钚堆plutonium burner钚回收plutonium recovery钚累积plutonium buildup钚平衡plutonium balance钚燃料堆plutonium-fuelled reactor钚循环plutonium cycle钚再循环plutonium recycle钚再循环能力capability for plulonium recycle钚增殖plutonium breeding部分半衰期partial halflife部分负荷运行part-load coperation部分快速停堆partial scram部分停堆partial shutdown部分终止合同partial termination of contract部件故障数据库component event date bankC材料辐照堆material processing reactor 材料试验堆materials testing reactor财务费用financial cost财务分析finance analysis财务净现值financial net present value财务内部收益率financial internal rate of return财务评价finance evaluation参考电站reference plant参考辐射reference radiation参考源reference source参考源响应reference response残余放射性residual activity仓储费godown charges舱hatch 操纵员引起的故障operator induced failure操纵员执照operator licence操作费用handling charges操作间隔operating compartment测量导管instrumentation thimble guide 测量堆measuring reactor层流laminar flow层流边界层laminar boundary layer层流对流laminar convection插棒速率speed of insertion插花式换料checker board refuelling插入程序insertion sequence插入深度depth of insertion插入深度insertion depth插入式封盖bayonet closure插入式取样器bayonet sampler差分放大器difference amplifier差压传感器differential pressure transducer差压发生器differential pressure producer差压流量计differential pressure flowmeter差压式仪表differential pressure instrumeatation柴油发电机组diesel set产钚堆plutonium-producing reactor产钚发电两用堆plutonium-and-power reactor产钚发电两用堆power-plus-plutonium reactor产地证书certificate of origin产额分布yield distribution产额截面yield cross section产额曲线yield curve产额因子yield factor长半衰期缓发中子long period delayed neutron长期低剂量照射prolonged low dose rate exposure长期反应性变化long-term reactivity change长期辐照long-term irradiation长期连续照射long continued exposure 长期照射long exposure长期照射long-term exposure长期中毒long-term poisoning长手套gaunlet长寿命放射性long lived radio activity长寿命辐射long lived radiation长寿命裂变产物long-live fission product长寿命同位素long lived isotope长寿期缓发中子long-lived delayed neutron偿还amortization偿还期pay off period偿还时间payback time偿还周期payback period偿债基金折旧sinking fund depreciation 常规岛conventional island常规监测routine monitoring常规通量密度conventional flux density 厂内事故on-site accident厂外电源off-site power厂外环境监视off-site environmental surveillance厂外事故offsite accident厂外应急计划off-site emergency plan厂用变压器auxiliary transformer厂用锅炉auxiliary boiler厂用配电装置auxiliary switchyard厂用水service water厂用蒸汽供应系统auxiliary steam supply system厂址相关极端事件site related extreme events场内应急计划on-site emergency plans场外监视offsite surveillance敞车交货价free on truck超负荷紧急停堆overload scram超高freeboard超高通量堆superflux reactor超高温堆ultra-high-temperature reactor 超高温气冷堆very high temperature gas cooled reactor超镉裂变epicadmium fission 超镉通量epicadmium flux超镉中子epicadmium neutron超功率紧急停堆overpower scram超功率事故保护停堆overpower trip超功率瞬态overpower transient超剂量overdosage超剂量事故照射accidental overexposure超剂量照射undue exposure超快中子ultrafast neutron超冷中子ultracold neutron超临界supercritical超临界的above-critical超临界的epicritical超临界质量above-critical mass超临界状态above-critical state超前控制advance control超热的epithermal超热俘获epithermal capture超热活性epithermal activity超热碰撞epithermal collision超热区epithermal region超热中子epithermal neutron超热中子反应堆epithermal reactor超热中子激活epithermal activation超热中子裂变epithermal fission超热中子漏失epithermal leakage超热中子吸收epithermal absorption超声检查ultrasonic inspection超声探头ultrasonic probe超瞬发临界super-prompt criticality超速跳闸overspeed trip超阈能量epithres hold energy超致死剂量supralethal dose撤离办法escape provision撤离计划evacuation plan撤离路线escape routes撤离区边界evacuating area boundary沉积床快中子堆settled bed fast reactor 沉积物积存fallout deposition沉降物取样网fallout sampling network 沉箱caisson衬里inner liner衬硼的boron lined成本分析breakdown of cost成本分析cost analysis成本加保险cost and insurance成本加运费cost and freight成本-利益分析cost-benefit analysis成本评估cost evaluation成本-效益分析cost-effectiveness analysis成熟堆型proven reactor type承付款项obligation incurred承诺commitment承运人carrier承重墙bearing wall城市生态学urban ecology澄清clarification弛压水池pressure suppression pool迟付deferred payment迟交货late delivery迟交货罚款late delivery penalty持久照射persistent radiation尺寸公差dimensional tolerance尺寸检查dimensional inspection尺寸完整性dimensional integrity充氦试验helium summation test充隋性气体安全壳inerted containment 抽查random inspection出口欠热度outlet subcooling出口信贷export credit出口许可证export license出入舱门access hatch出入闸门access lock出射剂量率dose rate out初成本initial cost初次临界first criticality初级辐射primary radiation初裂纹incipient crack初始initial初始堆芯initial core初始反应性initial reactivity初始沸点initial boiling point初始富集度initial enrichment初始过剩反应性initial excess reactivity 初始剂量initial dose初始碰撞initial collision 初始条件initial condition除氚detritiation除碘remove iodine除盐desalination除盐设备demineralization plant除盐水desalted water处置场disposal site处置区disposal area氚tritium氚放射性tritium activity氚含量tritium level氚核triton氚化tritiation氚监测器tritium monitor氚浓度tritium concentration氚增殖tritium breeding穿晶断裂transcrystaline fracture穿孔密封aperture seal穿透概率penetration probability传热机理heat transfer mechanism传热流体回路heat transfer fluid loop船边交货价free alongside ship垂直通量分布vertical flux profile磁粉探伤magnaflux inspection磁镜堆mirror reactor磁聚变能magnetic fusion energy次级辐射secondary radiation次级中子secondary neutron次临界subcritical次临界undercritical次临界堆subcritical reactor次临界反应convergent reaction次临界反应堆convergent reactor次临界反应性subcritical reactivity次临界冷堆cold subcritical reactor次临界平衡subcritical equilibrium次临界实验subcritical experiment次临界增殖因子subcritical multiplication factor次临界质量partial crit次临界装置subcritical facility次临界状态subcritical condition次热中子subthermal neutron粗调控制棒coarse control rod脆断强度brittle fracture strength脆化embrittlement脆性材料brittle material脆性断裂brittle fracture脆性故障brittle failure脆性破裂brittle rupture脆性-延性转变brittle-ductile transition D大部件试验回路large component test loop大会General Conference大量裂变产物bulk fission product大流量泵high capacity pump大破口large break大气放射性aeroadioactivity大气腐蚀atmospheric corrosion大气腐蚀outdoor corrosion大气监测air monitoring大气扩散atmospheric diffusion大气弥散atmospheric dispersion大气条件atmospheric conditions大气污染airborne contamination大气污染atmospheric contamination大气稀释atmospheric dilution大气中钚尘airborne plutonium大气中的放射性airborne radioactivity大气中氡放射性atmospheric radon activity大气中正常温度梯度lapse代理合同agency contract代理人attorney带包壳的棒canned rod带厂用电运行house load operation带汽率carryunder贷方credit贷款loan贷权人creditor单程操作single-pass operation单流程堆芯one flow core单流程堆芯single-pass core单能堆single-energy reactor单能中子single-end neutron单区堆single region reactor单速中子one speed neutron 单相临界流single-phase critical flow单向破裂single-end break单压堆one cycle reactor单一故障准则single failure criteria单一事件single event单一随机故障single random failure单源unisource弹棒事故control rod ejection accident弹棒事故rod ejection accident弹性散射elastic scattering弹性散射共振elastic scattering resonance氮气覆盖nitrogen blanket氘—氚反应堆deuterium-tritium reactor 氘核deuteron氘化deuterization氘化deuterize倒计数count down倒角芯块chamferred pellet到期付款payabled at maturity到期日due date到期日付款due date payment等剂量isodose等剂量图isodose chart等熵过程isoentropic process等效活度equivalent activity等效剂量equivalent dose等效裸堆equivalent bare core等效衰变常数equivalent decay constant 等效栅元equivalent cell低放废物箱low activity waste tank低放固体废物low-level solid waste低放实验室low-level laboratory低富集堆low enrichment reactor低富集燃料slighted enriched fuel低概率事件event of low probability低概率事件low probability events低功率堆low power reactor低能γ源low-energy gamma source低能中子low-energy neutron低浓缩度low enrichment低人口密度区zone of low population density低水平剂量计low-level dosimeter低温堆low temperature reactor低温气体贯穿件cold-gas penetration低压安全壳low pressure containment低压安全注入low pressure safety injection低压堆芯喷淋系统low pressure core spray system低压紧急停堆low pressure scram低压事故保护停堆low pressure trip低压应急冷却系统low pressure emergency cooling system低于临界below critical滴droplet底部反射层bottom reflector底部热屏蔽bottom thermal shield底部栅格板bottom grid底封头bottom head地表监测terrain monitoring地面安全壳above-ground containment 地面处置terrestrial disposal地面反应谱ground response spectrum地面试验堆ground test reactor地面污染监测仪floor contamination monitor地区应急控制中心local emergency operating centre地下处置区ground disposal area地下核爆炸contained nuclear explosion 地下核设施underground nuclear unit地下埋藏区burial ground地震地面运动earthquake ground motion 地震分析earthquake analysis地震加速度earthquake acceleration地震力earthquake force地震烈度earthquake intensity地震设计准则earthquake design criteria 地震危害earthquake hazard地震载荷earthquake loads第三方核责任nuclear third party liability第一炉料first core第一批浇灌混凝土first concrete缔约信件conclusion letters点堆point reactor 点扩散核point diffusion kernel点散射point scattering点散射体point scatterer点源point source点源剂量point-source dose碘反应器iodine reactor碘过滤器iodine filter碘化铯cesium iodide碘吸收器iodine absorber碘吸收器iodine trap电厂保卫plant security电厂放射性监测plant radiation monitoring电磁泵conduction pump电化学腐蚀electro-chemical corrosion 电缆穿墙cable penetration电缆贯穿件cable penetrator电离辐射ionizing radiation电离辐照ionizing irradiation电气贯穿件electrical penetration电渗析electric dialysis电涂覆electrocoating电站毛效率gross plant efficiency电子射线electronic rays电子微探针electron microprobe电子显微放射自显影法electron microautoradiography电阻探头法electricity resistance probe method调查水平investigation level调峰电站peak-load stations调节棒adjuster rod调节行程adjustment stroke调试commissioning test调试commissioning调试大纲commissioning programme调质铀adjusted uranium碟形底封头dished bottom碟形芯块dished pellet顶部加料top loading定位index motion定位格架grid spacer定向剂量当量directional dose equivalent动力堆power producing reactor动力堆power reactor动力矩kinetic moment动力增殖堆power breeder动力粘度dynamic viscosity动量kinetic momentum动密封dynamic seal动能kinetic energy动平衡dynamic balancing动态范围dynamic range动态分析dynamic analysis动态模拟试验dynamic analog test动态强度dynamic strength动态烧毁dynamic burnout动态试验dynamic testing动态稳定性dynamic stability动态响应dynamic response动压力dynamic pressure动压头kinetic head动载荷dynamic load动作时间actuating time毒物衰变poison decay毒物元件poison element独立裂变产额independent fission yield 端部热损失end heat loss端盖end cap短控制棒part-length rod短期照射过的short-irradiated短时间照射short-term exposure短寿命放射性short-lived radioactivity短寿命裂变气体short-lived fission gas 短寿命同位素short-lived isotope断裂abruption断裂边缘crack edge断裂强度fracture strength断流事故loss of flow accident煅烧炉calcinator堆动态性能dynamic behaviour of a reactor堆功率下降reactor rundown堆焊bead welding堆焊层overlay cladding堆积比重bulk specific gravity堆内in-core 堆内in-reactor堆内分析系统in-core analysis system堆内构件core structure堆内构件reactor internals堆内裂变产物总量in-core fission product inventory堆内汽水分离器internal steam separator 堆内热离子堆in-core thermionic reactor 堆内实验in-core experiment堆内探测器in-core detector堆内特性internal reactor characteristics 堆内通量探测器in-core flux detector堆内循环燃料internal fuel cycle堆年reactor year堆外测量仪表ex-core instrumentation堆外的out-of core堆外热离子堆out-of-core thermionic reactor堆外实验ex-reactor experiment堆外中子监测out-of-core neutron monitoring堆项目reactor project堆芯active core堆芯备用冷却系统core standby cooling system堆芯布置core configuration堆芯部件core internals堆芯测量仪表in-core instrumentation堆芯长度core length堆芯出口core exit堆芯出口平均含汽率core average exit quality堆芯出口温度core exit temperature堆芯出口压力core exit pressure堆芯等效直径equivalent core diameter 堆芯底板core bottom堆芯吊篮core barrel堆芯吊篮reactor core barrel堆芯吊篮壳体core barrel shell堆芯反射层core reflector堆芯分区core zoning堆芯峰值因子core peaking factor堆芯辅助冷却系统core auxiliary cooling system堆芯复合结构composite core structure 堆芯盖core head堆芯盖板core cover plate堆芯高度active core height堆芯高度core height堆芯功率分布core power distribution堆芯功率径向分布core radial power distribution堆芯功率密度core power density堆芯管core tube堆芯环段core shell堆芯夹具core clamp堆芯监测in-core monitoring堆芯结构reactor core structure堆芯解体reactor core disassembly堆芯解体事故core disassembly accident 堆芯进口core inlet堆芯冷却回路core coolant loop堆芯冷却剂流core coolant flow堆芯冷却剂流量coolant flow through the core堆芯内空泡分布core void distribution 堆芯内空泡份额core void fraction堆芯内空泡含量core void content堆芯能谱core spectrum堆芯浓度core concentration堆芯喷淋系统core spray system堆芯平均燃耗average core burnup堆芯平均热流密度core average heat flux堆芯欠热core subcooling堆芯区core region堆芯全部熔化事故core melt through accident堆芯裙筒core skirt堆芯燃料温度core fuel temperature堆芯热工设计core thermal design堆芯热工水力设计thermohydraulic core design堆芯热功率core thermal power堆芯容器core tank堆芯容器core vessel堆芯熔化core meltdown堆芯熔化reactor core meltdown 堆芯熔化分析core meltdown analysis堆芯熔化事故core meltdown accident 堆芯熔化现象core meltdown phenomena堆芯上部构件upper core internals堆芯设计core design堆芯升温事故core heat-up accident堆芯寿期core life堆芯水覆盖core water cover堆芯水力学core hydraulics堆芯水力学设计hydraulic core design 堆芯碎裂事故core disruptive accident堆芯损坏core damage堆芯通道core channel堆芯图core map堆芯外ex-core堆芯完整性core integrity堆芯围板core baffle堆芯围板reactor core baffle堆芯围筒core shroud堆芯围筒inner shroud堆芯稳定度core stability堆芯物理core physics堆芯性能恶化事故degraded core accident堆芯循环core cycle堆芯压降core pressure loss堆芯压降reactor core pressure drop堆芯压力容器core pressure vessel堆芯淹没core deluge堆芯淹没系统core deluge system堆芯淹没系统core flooding system堆芯仪表系统in-core instrumentation system堆芯有效流通面积effective flow area of core堆芯元件core element堆芯再淹没core reflooding堆芯栅板core grid堆芯栅板diagrid堆芯栅格active lattice堆芯栅格core cell堆芯栅格core lattice堆芯栅阵core matrix堆芯支承reactor core restraints堆芯直径active diameter堆芯直径core diameter堆芯总流量total core flow rate堆芯总压降total core pressure drop堆中毒poisoning of a reactor堆中子谱pile spectrum对比研究comparative study对环境的危害hazard to the environment 对流通量convective flux对人员的危害hazard to personnel对销供货countersupply多板裂变室multiplate fission chamber 多层安全壳multiple barrier containment 多层安全壳multiple containment多次剂量multiple dose多次碰撞multiple collision多次碰撞概率maltiple collision probability多次事件multiple events多道屏障successive barriers多堆核电站multi-reactor nuclear power plant多分包合同multiple package contract多环路安全系统multi-loop safety system多孔堆porous reactor多孔热绝缘poros thermal insulation多普勒常数Doppler constant多普勒反馈Doppler feedback多普勒位移Doppler displacement多普勒效应Doppler effect多区堆multiple region reactor多区堆芯multiregion core多群中子扩散方程multigroup neutron diffusion equation多相扩散multiphase diffusion多用堆multipurpose reactor多用途核电站multipurpose nuclear station多用研究堆multipurpose research reactor多重故障compound malfunction多重故障multi-failure 多重屏障multibarrier多重屏障系统multibarrier system多重子系统redundant subsystem堕落硬度试验drop hardness test惰性裂变气体noble fission gas惰性气体放射性noble gas activity惰性气体裂变产物inert gas fission product惰性气体裂变产物noble gas fission product惰性气体同位素noble gas isotope惰走coastingE俄罗斯原子能出口公司Atomenergoexport额定功率降低derated power额外索取extra levy额外折扣exceptional discount额外中子extra neutron二次安全壳secondary containment二次能源derived energy二次屏蔽secondary shielding二次源secondary source二次源棒secondary source rod二取一系统one out of two system二氧化碳冷却堆carbon dioxide cooled reactor二氧化铀陶瓷芯块ceramic UO2 pellet 二氧化铀芯块uranium dioxide pelletF发电堆electricity production reactor发光放射自显影探测lumoautoradiographic detection发光检查luminescent inspection发光涂料luminescent paint发货人consignor发票invoice发射裂变emissive fission发执照者licensor乏燃料burned-up fuel乏燃料burnt-up fuel乏燃料irradiated fuel乏燃料spent fuel乏燃料操作机spent fuel manipulator乏燃料池spent fuel pool乏燃料处置spent fuel disposal乏燃料罐spent fuel flask乏燃料后处理irradiated fuel reprocessing乏燃料后处理spent fuel reprocessing乏燃料就地贮存on-site spent fuel storage乏燃料冷却水池spent fuel pit乏燃料运输罐irradiated fuel shipping cask乏燃料贮存irradiated fuel store乏燃料贮存spent fuel storage乏燃料组件irradiated fuel assembly乏燃料组件spent fuel assembly筏基bottom raft法兰密封引漏系统flange leak-off system法人实体body corporate反常性abnormality反扩散涂层antidiffusion coating反散射因子backscatter factor反射层慢化反应堆reflector moderated reactor反向洗涤backflush反应堆reactor反应堆安全reactor safety反应堆安全分析reactor safety analysis 反应堆安全壳reactor containment反应堆安全壳边界reactor containment boundary反应堆安全系统reactor safety system反应堆保护系统reactor protection system反应堆边界reactor boundary反应堆变量reactor variables反应堆操纵平台reactor operating floor 反应堆操纵员reactor operator反应堆厂房reactor building反应堆厂房吊车reactor building crane 反应堆厂房喷淋系统reactor building spray system反应堆衬里reactor liner反应堆动力学reactor dynamics 反应堆动态性能dynamic reactor behaviour反应堆毒物reactor poison反应堆堆内构件reactor core internals反应堆堆芯reactor core反应堆堆芯寿期lifetime of reactor core 反应堆辅助厂房reactor auxiliary building反应堆辅助系统reactor auxiliary system反应堆给水reactor feedwater反应堆工艺reactor technology反应堆功率剧增reactor excursion反应堆功率剧增事故reactor excursion accident反应堆化学reactor chemistry反应堆级order of reactor反应堆监视reactor surveillance反应堆结构reactor construction反应堆紧急停堆reactor scram反应堆紧急停堆系统reactor scram system反应堆静力学reactor statics反应堆可利用率reactor availability反应堆控制reactor control反应堆冷却剂reactor coolant反应堆冷却剂回路reactor coolant loop 反应堆理论reactor theory反应堆裂变碎片reactor debris反应堆模拟机reactor simulator反应堆平均温度average reactor temperature反应堆平均温升average reactor temperature rise反应堆屏蔽reactor shielding反应堆启动reactor start-up反应堆启动速率reactor start-up rate反应堆启动源reactor source反应堆全堆计算global reaction calculation反应堆燃料reactor fuel反应堆燃料熔化reactor meltdown反应堆容器reactor vessel反应堆失控reactor runaway反应堆事故reactor accident反应堆瞬态行为reactor transient behaviour反应堆停堆reactor shutdown反应堆稳定性reactor stability反应堆卸压depressurize a reactor反应堆压力容器设计reactor vessel design反应堆严重事故reactor disaster反应堆应急停堆reactor emergency shutdown反应堆运行班长chief reactor operator反应堆再启动reactor restart反应堆噪声reactor noise反应堆增殖reactor multiplication反应堆振荡器reactor oscillator反应堆制造商reactor manufacturer反应堆中毒reactor poisoning反应堆中心通量central reactor flux反应堆中子能谱reactor neutron spectrum反应堆中子谱仪pile-neutron spectrometer反应堆中子物理学pile-neutron physics 反应堆最优化reactor optimization反应率reaction rate反应谱response spectrum反应谱分析response spectrum analysis 反应热heat of reaction反应性reactivity反应性白噪声white reactivity noise反应性变化reactivity change反应性变化reactivity variation反应性变化率reactivity rate反应性补偿reactivity compensation反应性补偿reactivity shimming反应性测定仪reactimeter反应性储备reactivity reserve反应性单位reactivity unit反应性单位(=10-5)pour centmille反应性当量reactivity equivalent反应性的有效性reactivity efficacy反应性调节reactivity regulation反应性反馈reactivity feedback 反应性功率系数power coefficient of reactivity反应性贡献reactivity contribution反应性急变reactivity surge反应性减少量decrement in reactivity反应性阶跃变化reactivity step change 反应性控制reactivity control反应性亏损deficit reactivity反应性谱reactivity spectrum反应性扰动reactivity disturbance反应性事故reactivity accident反应性释放reactivity release反应性寿命reactivity life反应性寿期reactivity lifetime反应性瞬态reactivity transient反应性速降prompt drop of reactivity反应性损失loss of reactivity反应性损失reactivity loss反应性线性增加reactivity ramp反应性效应reactivity effect反应性引入insertion of reactivity反应性引入reactivity insertion反应性约束reactivity binding反应性跃变reactivity jump反应性增加reactivity increase反应性增量reactivity increment反应性增益reactivity gain反应性振荡器reactivity oscillator反应周期reaction period方案设计conceptual design方案设计阶段concept phase方框图block diagram防尘的anti-dusting防毒面具gas mask防飞射物missile proof防浮levitation safeguard防辐射的radiation proof防护代价cost of protection防护最适剂量optimal dose for protection防火屏障fire stop防松螺母jam nut防污染标准anti-pollution standard防污染装置antipollution device仿效机械手slave manipulator放射毒理学radiotoxicology放射分析radioanalysis放射生态学radioecology放射生物测定radiobioassay放射性半衰期radioactive half-life放射性比activity ratio放射性测量仪activity meter放射性产物active product放射性车间hot shop放射性尘埃active dust放射性沉淀物active deposite放射性沉降物active fall-out放射性纯度radioactive purity放射性碘radioactive iodine放射性毒物radioactive poison放射性放出activity escape放射性废物active waste放射性废物hot waste放射性废物radioactive waste放射性废物处理系统radwaste system放射性废物桶封盖drum closing放射性辐照activating radiation放射性含量radioactive content放射性核素radionuclide放射性灰radioactive ash放射性灰尘radioactive dust放射性夹杂物radioactive inclusion放射性监测activity monitoring放射性氪radiokrypton放射性氪同位素radioactive krypton isotope放射性累积activity build-up放射性裂变产物radioactive fission product放射性裂变产物释放active fission product release放射性裂变产物逸出escape of radioactive fission products放射性裂变气体radioactive fission gas 放射性浓度activity concentration放射性排出物active effluent放射性排出物处置active effluent disposal 放射性排放activity discharge放射性排放hot drain放射性排放系统active effluent system 放射性平衡radioactive equilibrium放射性气溶胶radioactive aerosol放射性气溶胶radioaerosol放射性气体radgas放射性气体radioactive gas放射性区active region放射性区hot zone放射性区衣柜hot wardrobe放射性区域active zone放射性取样设备active sampling equipment放射性去污radioactive decontamination 放射性热radioactive heat放射性实验室hot laboratory放射性示踪剂radioactive tracer放射性事故activity accident放射性试验室active laboratory放射性释放released of radioactivity放射性疏水泵active drains pump放射性疏水箱active drains tank放射性衰变activity decay放射性衰变radioactive decay放射性水activated water放射性水平activity level放射性水平level of activity放射性水平radioactive level放射性碎片radioactive debris放射性损伤radioactive damage放射性同位素radioisotope放射性维修车间active workshop放射性维修间hot workshop放射性污染radioactive contamination放射性洗衣房active laundry放射性洗衣房hot laundry放射性氙radioxenon放射性泄漏radioactive leak放射性药物radioactive drug放射性液态废物系统liquid radwaste system放射性元素radioelement放射性杂质activated impurity。

critical disability study

critical disability study

critical disability studyCritical disability studies is an interdisciplinaryfield of study that examines the social, cultural, and political factors that shape and construct disability. It challenges dominant narratives and representations of disability as individual deficits or medical conditions, and instead focuses on understanding disability as a social and political phenomenon rooted in systems of power, oppression, and discrimination.Critical disability studies seeks to center the experiences and perspectives of disabled people, working to address and dismantle societal barriers and inequalities that perpetuate the marginalization and exclusion of disabled individuals. It critiques ableism, which refers to the discrimination and prejudice faced by disabled people based on assumptions of normalcy and superiority of non-disabled bodies and minds.This field of study draws on various theoretical perspectives, including social constructionism, intersectionality, and poststructuralism, to examine the ways in which disability is produced, constructed, and understood within different social, cultural, and historical contexts.It also explores the intersections of disability with other forms of oppression, such as race, gender, sexuality, and class, and seeks to challenge the hierarchies and power imbalances that exist within these intersecting systems of oppression.Through critical analysis of disability policies,narratives, and representations, critical disability studies works to advocate for social justice and the creation of inclusive, accessible, and equitable societies for all individuals, regardless of their disability status. It aims to shift the focus from individualistic approaches to disability towards systemic and structural changes that promote the full participation and empowerment of disabled people in all aspects of society.。

LETTER TO THE EDITOR Percolation and conduction in a random resistor-diode network

LETTER TO THE EDITOR Percolation and conduction in a random resistor-diode network

These elements occur with random probabilities d,, d-, r and v respectively. For this system, the diode ‘polarisation’ points along an axis inclined at 45”to the horizontal, taking on any value between -1 and + l . Our work indicates that this model exhibits novel phase transitions due to the formation of infinite clusters which support either isotropic information flow or unidirectional flow, either with or against the diode polarisation. We have applied the position-space renormalisation group (PSRG) to study the properties of this random resistor-diode network. Our procedure is based on the simplest approximation of rescaling a 2 x 2 bond cell as shown in figure 1 (Reynolds et a1 1977). For the 45 configurations of the cell, we calculate the probabilities of traversing the cell in both directions, and in only one direction. These give respectively, the probability of a renormalised resistor, and the probability of a renormalised diode oriented in the direction of traversing. From these recursion relations, we obtain the phase diagram in the probability space spanned by d,, d-, r and v (figure 2). Four phases exist: a ‘vacancy’ phase containing only finite clusters, a ‘resistor’ phase in which information flows isotropically within the infinite cluster, and two unidirectional ‘diode’ phases in which information flows only along the direction of diode polarisation. The phase diagram exhibits two symmetries which arise from the invariance of the recursion relations under inversion (d+-d-), and under a duality in which v - r and d,-d,. The latter symmetry appears to be exact, similar to the dual symmetry of pure bond percolation. Of the six non-trivial fixed points (figure 2), there are two directed fixed points which occur at d: (or d ? ) = 0.5550, U * = 1- d z , and r* = 0. They describe the onset of an infinite cluster which transmits only along the direction of diode polarisation. Our value of d* is a reasonable approximation to the estimates d , = 0.643-0.645 for directed percolation found by more accurate numerical methods (Blease 1977a, b, c, Kertksz

关于误差规律性与影响特性的新概念The new concept of measurement

关于误差规律性与影响特性的新概念The new concept of measurement
The standard deviation of deviation ΔA is given by the statistic and analysis of current measurement data. The deviation ΔB is also produced by measurement; its formation principle is actually the same as the current measurement; its standard deviation can be obtained by tracing back to its upstream measurement. Thus, the standard deviation
Measurement 126 (2018) 65–71
Contents lists available at ScienceDirect
Measurement
journal homepage: /locate/measurement
The new concepts of measurement error’s regularities and effect T
For example: in 2005, the Chinese surveying and Mapping Bureau gave that the elevation result of Mount Everest is 8844.43 m with standard deviation of ± 0.21 m. According to existing error classification theory, from the perspective of error’s definition, the error of this result is a single constant deviation and should be classified as systematic error; however, from the perspective of standard deviation ± 0.21 m, it should be classified as random error. This is the logical trap of existing error classification theory. And the interpretation, according to error non-classification theory, is that this result's error (the difference between the result and the true value at implementing measurement) is an unknown constant, and that the standard deviation of ± 0.21 m is only the evaluation of the probable interval of the unknown

Deductive and inductive

Deductive and inductive
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Deductive and Inductive: Types of Validity, Not Types of Argument
David Hitchcock McMaster University
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pressure ridge coming from a different directionl make it highly unlikely that it will rain tomorrow. Then, despite the truth of the premises, the conclusion is false. In general, traditionally inductive arguments of this sort become deductively valid only if we stipulate that the premises describe a closed system or we add an open-ended premise to the effect that no other factors obtain which would make the predicted state of affairs improbable. But adding such premises changes the traditionally inductive argument into a traditionally deductive one. Hedging the conclusion of a traditionally inductive argument in fact involves a claim about the strength of the link between the evidence cited in the premises and the occurrence predicted in the conclusion. Since there may be uncited counter-evidence, the predicted occurrence may be in reality highly improbable, even though the premises provide probable grounds for thinking it will occur. Although Weddle's elimination of the distinction fails, there are good arguments against three traditional ways of defining it: in terms of logical form, in terms of the strength of the link between premise(s) and conclusion, and in terms of the claimed or intended strength of this link. Weddle (5) himself provides convincing counter-examples to attempts to make the distinction on the basis of logical form, such as the contention that inductive arguments draw universal conclusions from particular premises and deductive arguments draw particular conclusions from universal premises. Skyrms (4, pp. 13-15) gives examples of all possible combinations of particular and universal statements in both deductively valid and inductively strong arguments. Fohr (1) rightly points out that a distinction in terms of the strength of the link between premises and conclusion runs foul cf the requirement that there can be bad, i.e. invalid or weak, instances of each type of argument. Arguments which are neither deductively valid nor inductively strong (nor conductively valid, etc.) will have no place in a supposedly exhaustive classification. One way of patching up this approach is to label "inductive" all arguments which are not deductively valid, but, as Weddle (5) notes, the practice of logic texts indicates that this is not how logicians make the distinction. Most recent logic texts define deductive arguments as arguments which involve the claim that the conclusion follows necessarily from the premises, and inductive arguments as arguments which claim only that the premises provide probable grounds for the conclusion. Fohr's (.1) proposal to base the distinction on whether the person putting forward the argument intends his premises to provide conclusive or merely probable grounds for the conclusion is a variant of this approach, for the only way of detecting such intentions is to notice what·the arguer claims. Although this third type of proposal escapes the objections to the two previous approaches, there are two strong arguments against it. In the first place, as Weddle (5) points out, the claimed or intended strength of the
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where µ is positive and is a function of the density. Since there is a characteristic occupation this is referred to as the fluid phase. As the density increases towards the critical value ρc , µ tends to zero and the resulting distribution becomes a power law at ρ = ρc . For ρ > ρc an extra piece of p(n), representing a single condensate, emerges centered at n = L(ρ − ρc ) [16]. Thus in the condensed phase a critical fluid co-exists with a condensate containing the excess density. A pure power-law distribution only holds at the critical density which is a common feature in many systems exhibiting phase transitions. For b < 2 there is no condensation transition since any density can be achieved by choosing µ to be suitably small in (1).
arXiv:0705.4042v2 [cond-mat.stat-mech] 8 Aug 2007
Criticality and Condensation in a Non-conserving Zero Range Process
A. G. Angel1,2 , M. R. Evans2 , E. Levine3 and D. Mukamel4
1
PACS numbers: 89.75.-k, 05.70.Ln, 05.40.-a
Criticality and Condensation in a Non-conserving Zero Range Process 1. Introduction
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There exist many systems exhibiting real-space condensation under nonequilibrium steady state conditions. Examples include jamming in traffic flow, granular clustering, wealth condensation and gelation in networks [1]. Real-space condensation implies that a finite fraction of some conserved quantity, for example density, condenses onto a single lattice site or a small region in space. In general one is interested in the distribution of the conserved quantity and the emergence of the condensate as some parameter, often the density, is varied. The Zero-Range Process (ZRP) [2] is a generic model which exhibits condensation in its nonequilibrium steady state [3, 4]. Moreover it has the convenient property that its steady state is known and has a simple factorised form. Thus the ZRP provides a simple exactly solvable model within which general features of condensation may be studied and analysed [1]. For example, recent developments include: extensions of the model to several conserved quantities [5, 6, 7], open boundary conditions [8], and sitewise disorder [9, 10, 11]; the study of current fluctuations [12] and traffic modelling [13, 14]. The ZRP is usually defined on a lattice of L sites where each site may be occupied by any integer number of particles. The dynamics is defined by hopping rates u(n) with which a particle hops from a site occupied by n particles. In various versions of the dynamics the particle may hop to different allowed destination sites. For example on a regular lattice particles hop to nearest neighbour sites whereas on a fully-connected geometry a particle can hop to any other site with equal probability. Clearly, the total number of particles, N , is conserved under the ZRP dynamics. Condensation occurs when in the large N , L limit, with the density ρ = N/L held fixed, a finite fraction of the particles condenses onto a single lattice site. More recently, an example where the condensate has a non-zero spatial extent has been studied [15]. Condensation is revealed in the single-site occupation probability distribution, p(n). A characteristic case is when the hopping rate has the asymptotic, large n form u(n) ≃ 1 + b/n. For b > 2, the model exhibits a condensation transition at a critical density ρc . For ρ < ρc , p(n) has the form p(n) ∝ n−b e−µn (1)
Criticality and Condensation in a Non-conserving Zero Range consider more general dynamical processes which could allow for more complex condensation phenomena. Examples of the phenomena we have in mind are the existence of criticality in an extended region of the phase diagram rather than at an isolated point (typically referred to as self-organised criticality), and condensation into a large number of condensates each containing a subextensive number of particles. In our generalised dynamics we introduce non-conserving processes with creation and annihilation rates. One mechanism to suppress a single extensive condensate is for the annihilation of particles to occur preferentially at highly occupied sites. We find that an appropriate choice of creation and annihilation rates leads to a whole critical region of the phase diagram where the occupation distribution decays algebraically at large occupations. Since the density is not conserved the phase diagram is given in terms of the parameters of the creation and annihilation rates. Let us briefly summarise the phases which are exhibited (see Fig. 1). As might be expected, for imbalanced creation and annihilation rates we find regimes with vanishing or diverging density. These two regimes are separated by phases where the observed density is equal to what would be the critical density on a conserving system and power-law occupation distributions are exhibited. One of these phases, Critical Phase A, exhibits a pure power-law distribution for p(n) with a cut-off diverging with system size. However another region in parameter space exists where the distribution exhibits, in addition to the power-law decay, a broad and weak peak at high occupations. The height of the peak scales algebraically with system size, rather than exponentially, as does the width. This peak may correspond to many ‘mesocondensates’ each of which contains a subextensive number of particles. The number of these mesocondensates is also subextensive thus they occupy a vanishing fraction of the sites. We shall give a detailed analysis of this weak peak and how it leads to two phases: Critical Phase B where the weak peak does not contribute to the global density which is ρc and the Weak High Density Phase where the contribution of the weak peak to the global density is dominant. In a recent publication [17] we gave a brief account of the non-conserving ZRP and its relation to self-organised criticality and the dynamics of rewiring networks. Here we focus on the properties of the non-conserving ZRP and present a detailed analysis of the phase diagram. The structure of the paper is as follows: in Section 2 we define the non-conserving ZRP that we study; in Section 3 we present a detailed analysis of the phase diagram via a mean-field approximation and we compare the results to numerical simulations on fully-connected and one-dimensional lattices; we conclude with a discussion in Section 4. 2. Definition of non-conserving ZRP We now define the non-conserving zero-range process which we study in this work. The lattice contains L sites labelled l = 1, . . . , L. The number of particles at site l is nl . The dynamics are defined by the following three processes: particles hop from a site with n
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