Part 66 B2 Modules
Karola Mura
Perhaps the question should be: How can I tell what modules were originally provided with the specific Perl installation on a machine? (Actually, it is now asked as How can I tell what modules were originally provided with the specific Perl installation on a machine?.)
Given that there now appears to not to be an overall Perl standard installation, at least the answer to this new question will tell me what I originally had in the installation when it was first installed.
With that knowledge and if I keep the original installer image/package OR know how to get the exact thing again online, then I have a repeatable Perl installation for several machines with the knowledge of what modules will be present and what modules will not.
I asked spin-off question:How can I tell what modules were originally provided with the specific Perl installation on a machine? (How can I tell what modules were originally provided with the specific Perl installation on a machine?)
Installations that do not contain these items are non-standard. Yes, I appreciate that it may seem academic from your perspective, but your vendor's packaging permitted a non-standard installation that breaks otherwise working programs.
There really is no such thing as "core" any more. There used to be a standard Perl distribution, but a lot of people don't have a standard Perl distribution. Operating system distributions modify it by either adding or removing modules, changing modules, and so on. You can't rely on the standard distribution being actually standard. Some Linux distributions don't even include the Perl documentation as part of the base Perl installation.
If your goal is to find out on specific machines, I would use the tools that come with the platform. On Debian, that would include dpkg (pre-installed on any Debian system) or apt-file (not pre-installed necessarily) or other APT tools.
This module outlines the differences between the IQ-achievement discrepancy model and the response-to-intervention (RTI) approach. It also offers a brief overview of each tier in the RTI model and explains its benefits (est. completion time: 1 hour).
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Behaviour is added to parts in KSP using modular components called part modules. These are classes which derive from PartModule. Multiple simple modules can be added to parts to build up complex behaviour. For example, the J-90 "Goliath" Turbofan Engine uses ModuleResourceIntake, ModuleEnginesFX, ModuleAnimateHeat, ModuleAnimateGeneric, FXModuleAnimateThrottle, ModuleJettison, FlagDecal, ModuleAlternator, ModuleTestSubject and ModuleSurfaceFX to provide its air intake, engine thrust and effects, heat effects, thrust reverser, moving engine fan, fairings, mission flag, electric charge generation, test missions and near-ground effects in a single part.
Part modules can be added to a part by editing that part's configuration file. For example, to add a part module called "ModuleName" to a part, the part's configuration file should be edited to include the following before the final closing '}' in the file:
If you prefer the tutorial approach to learning, the following links will walk you through a specific pair of tasks to introduce you to this system. If you prefer a methodical reference approach, skip the tutorials and read on, then come back to the tutorials afterward.
They all return a List of Parts rather than just one single part. This is because any name could have more than one hit. If you expect to get just one single hit, you can just look at the zero-th value of the list, like so:
For even more advanced part selection you can use the *PATTERN variants of the suffixes mentioned above (see Vessel:PARTSTAGGEDPATTERN, Vessel:PARTSTITLEDPATTERN, Vessel:PARTSNAMEDPATTERN and Vessel:PARTSDUBBEDPATTERN). They enable you to select parts based on regular expression matching, giving you ultimate power over your parts.
Difference between a KSPEvent and a boolean KSPField: If you see a label next to a button in the RMB context menu, it might be a KSPEvent, OR it might be a boolean KSPField variable which is editable with a tweakable GUI. They look exactly the same in the user interface. To tell the difference, you need to look at what happens when you click the button. If clicking the button causes the button to depress inward and stay pressed in until you click it again, then this is a boolean value KSPField. If clicking the button pops the button in and then it pops out again right away, then this is a KSPEvent instead.
A: Use the part.cfg file All parts in KSP come with a part.cfg file defining them, both for modded parts and stock parts. If you look at this file, it will contain sections looking something like this:
B: Use the :MODULES suffix of Part: If you have a handle on any part in kOS, you can print out the value of :MODULES and it will tell you the string names of all the modules on the part. For example:
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Students will receive an emails with information about the POOM and notifying them when each part of the POOM is open. Students will be reminded before the closing date if they have not yet completed a section of the POOM.
End-of-life management is important for addressing large future photovoltaic (PV) waste volumes and conserving raw materials for use in new PV modules. In regions without regulatory mandates for PV recycling, end-of-life PV modules can be disposed in accordance with general waste laws. Given the use of various metals as raw materials in semiconductor compounds and electrical contacts in commercial PV modules, some stakeholders have raised concerns regarding potential environmental impacts if PV modules are subject to improper disposal instead of being recycled or disposed in sanitary landfills, as is required in most world regions. To evaluate these concerns, screening-level risk assessment methods are developed herein that evaluate potential human health risks from groundwater and surface (air, soil, surface water) exposure pathways. The methods estimate potential impacts from disposal of end-of-life (EOL) PV modules in non-sanitary landfills under the following worst-case conditions: no leachate collection or groundwater monitoring, no liner for preventing leachate migration, uncovered waste, and lack of stormwater management. Examining worst-case conditions allows the exploration of maximum potential risk to attempt to ensure disposal does not increase health risk above regulatory thresholds.
Specifically, this report presents an analysis of potential human health risks associated with non-sanitary landfill disposal for three PV technologies, focusing on release of the highest-prioritized chemical element for each: lead (Pb) in crystalline-silicon (c-Si) PV modules, cadmium (Cd) in thin film cadmium telluride (CdTe) PV modules, and selenium (Se) in thin film copper indium selenide (CIS) PV modules. The prioritization of these chemical elements for analysis is based on stakeholder interest. Because the methodology is chemical-specific, the risk assessment results for these chemicals cannot be directly generalized to other chemicals, although the risk assessment methodology can be applied to other chemicals. If the chemicals chosen are indeed the ones presenting greatest risk, then the results herein should represent the upper bound of health risk from exposure to a single constituent.
Under the layers of health-protective assumptions applied, for Pb for c-Si PV, Cd from CdTe PV and Se from CIS PV, cancer risks and non-cancer hazards are found to be at least one order of magnitude below the US regulatory screening thresholds of 110-6 cancer risk and non-cancer hazard quotient of 1. Health screening levels can differ by country or region; exposure-point concentrations in groundwater and surface water of Pb, Cd, and Se for c-Si, CdTe, and CIS PV, respectively, are also within water quality guidelines from the World Health Organization. The results presented herein do not represent a complete human health risk assessment for PV module disposal nor an assessment of cumulative risk, although the results are suggestive of low risk for the prioritized chemicals examined using best available regulatory methods. The screening-level methods employed in this report can be used in future work to assess potential health risks from other chemicals of potential concern and other PV technologies to establish a more complete set of results for chemicals of potential concern.
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