Wednesday, February 27, 2008

How To Round 8.84 To Nearest Tenth

CONTROL RADIOACTIVE CONTAMINATION OF FOOD AND LIQUID ENERGY-CONTROL CERTIFICATION


OCCUR WITH ANY SPECIAL EQUIPMENT CONTAMINATION OF FOOD AND LANDFILL SITES SUBJECT TO ABUSE.

INSTRUMENTS TO HEAD BRITISH ARMY .-

CONTAMINATION DETECTION BY RAY: ALPHA BETA GAMMA

RICHIEDETE TRAMITE EMAIL PREVENTIVI DI SPESA : caso.gianfranco@virgilio.it


ENTRA NEL SITO DELL'ENEA TI FARAI UN'IDEA DI CIO' CHE STIAMO PARLANDO





Saturday, February 23, 2008

Sea Ray 270 Slx Problems

FLUES



RICHIEDI UNA CONSULENZA SULLA DETRAZIONE FISCALE DEL 55%

CONSULENZE TECNICHE PER LA CERTIFICAZIONE ENERGETICA PER AVERE DIRITTO ALLA DETRAZIONE FISCALE 55%



IL COSTO DI UNA CERTIFICAZIONE ENERGETICA DI UN IMMOBILE VARIA DA € 400


LINK PER CALCOLO VELOCE DI RESISTENZA TERMICA
http://www.isolparma.it/calcoloresistenza/calcola.asp


VIDEOISPEZIONE CANNE FUMARIE COSTI DA UN MINIMO DI 350€ A 500€

CONTROLLO ACQUA POTABILE CON ANALISI CHIMICHE E VIDEOISPEZIONE POZZO ARTESIANO

PREVENZIONE INCENDI RINNOVI E NUOVI RILASCI

RICHIESTE ECONOMICHE NON ESAGERATE

RICHIEDI UN PREVENTIVO PER LA SOLVING YOUR PROBLEMS

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http://it.wikipedia.org/wiki/Risparmio_energetico

Ministerial Decree 19 February 2007 "Provisions relating to deductions for the costs of upgrading the energy efficiency of existing buildings, according to Article 1, paragraph 349, of Law December 27, 2006, No 296 "provides for the deduction of the gross for a share of 55% of the costs incurred for the work: • energy upgrading existing buildings (Section 344 of the Finance and Art. 6 of DM 19 February) up to a maximum amount of 100,000 € • the wrapping of existing buildings (Section 345 of the Finance and Art. 7 of DM 19 February) to maximum amount of 60,000 €, ie - spoke for greater insulation of opaque vertical closure to the values \u200b\u200bgiven in Appendix-D for replacements of windows including frames • work to install solar panels in existing buildings (Section 346 of the Finance and Art. 8 of DM 19 February) up to a maximum amount equal to 60,000 € • interventions for the replacement of air space heating in existing buildings (Section 347 of the Finance and Art. 8 of DM 19 February) up to a maximum amount of 30,000 €. The formalities and documentation to be submitted for each of these interventions in order to obtain the deduction is described in Art. 4 of Decree 19 February 2007, and consists of: • a certified affidavit of compliance stating that the requirements in Articles 6, 7, 8 and 9 depending on the type of interventions • documents to be transmitted through the website www ENEA . acs.enea.it, namely: - copies of energy performance certificates, if they are present certification systems identified by region, province or autonomous local authorities, ovvero copia dell’Attestato di Qualificazione Energetica così come riportato nell’Allegato A – scheda informativa relativa agli interventi realizzati Allegato E• pagamento delle spese sostenute mediante bonifico bancario o postale “dal quale risulti la causale del versamento, il codice fiscale del beneficiario della detrazione ed il numero di partita IVA, ovvero, il codice fiscale del soggetto a favore del quale il bonifico è effettuato“ (art. 4 comma 1 lett. c DM 19 febbraio 2007)• conservare la documentazione di cui sopra ai fini degli accertamenti da parte degli uffici finanziari.L’asseverazione dell’intervento può coincidere con l’Attestato di qualificazione energetica dell’edificio as implemented, certified by the Director of Works. So, in order to obtain the deduction of 55% must be respect for the legalization of the minimum requirements of the DM 19 February 2007, by: • sworn report by a qualified professional qualification certificate • energy in art. 8 paragraph 2 of legislative decree 192/05 by the Director legalization of work, corresponding to what is contained in Annex A of this Decree; • certification by the manufacturer, in the case of replacement windows and replacement of the generator. The Qualification Certificate Energetics, Annex A, provides for any type of surgery, is indicated in the results: • the requirement primary energy for space heating (kWh / year) • the index of energy performance for space heating your building (or kWh/m2/year kWh/m3/anno) • the relevant limit value index provide energy for winter heating limit your building (or kWh/m2anno kWh/m3anno). You must bring to each type of intervention? The requirements identified article 4 of the decree provide for the purposes of the affidavit of assistance, to use the certification of producers, but for the purpose of communication is necessary to identify and compile ENEA the Qualification Certificate for each Energy intervention, and then determine the values \u200b\u200babove. In the case of upgrading the energy efficiency of the qualified professional affidavit shows the values \u200b\u200bof EP and coincides with the calculations required for the project. For other measures, allowed the deduction does not necessarily need to perform the calculation of energy performance, but you must bring these values \u200b\u200btherein. How do you calculate these values? Among the methods for assessing the energy performance of the decree refers to Annex B for a simplified procedure particularly suitable for the assessment, as detailed in note 25 of Annex A. The simplified procedure of Annex B proves useful especially for: • any replacements of windows, where you can make the certification by the manufacturer • work on the building envelope where calculations and asserts only the transmittance of the wall • solar panels made in self-certified system components for the interventions relating to the installation of solar panels, especially if integrated with the existing heating system, or replacement of air conditioning equipment for proper planning is well run the project and the related calculations. If the features do not make intervention necessary to run a project you can still use the simplified method to calculate the values \u200b\u200bmentioned in the certificate of qualification Energy. Description Annex B simplified DM 19 February 2007 simplified calculation procedure for obtaining a value greater than the limits set by law and is applicable only for the purposes of the application of deductions of 55% for interventions under the Ministerial Decree of February 19 2007.L ' process of the calculation procedure includes: 1) the determination of the thermal zone based on the type of facility and the calculation of the dispersant on the surface of the gross floor area and volume 2) the determination of thermal transmittance of opaque and transparent closures vertical and horizontal bounding surface dispersant 3) la determinazione della trasmittanza globale dell’edificio Ug, e della trasmittanza globale limite dell’edificio Uglim, e il coefficiente correttivo dimensionale CCtrasm4) la determinazione del rendimento termico utile alla potenza nominale del generatore di calore installato (dalla targa del generatore di calore), il rendimento minimo missibile ηlim, e il coefficiente correttivo dimensionale CCimp 5) la determinazione del coefficiente correttivo dimensionale CCglob. e dell’indice di prestazione energetica per la climatizzazione invernale EPi,c da attribuire all’edificio e riportare sull’Attestato di Qualificazione Energetica espresso in kWh/anno in kWh/m2/anno (o kWh/m3/anno), in base al valore dell’EP limit set out in Annex C depending on the intended use, by interpolation. Determination of surface area and thermal dispersant
The thermal zone is determined by the type of the heating system: centralized or autonomous. In the case of the autonomous system thermal zone coincides with the real estate unit. In the case of the centralized system thermal zone coincides with the whole building or part of a building served by Central. The surface area of \u200b\u200bthermal dispersants are calculated to the center of the closure of the border (closed vertical or horizontal). The surfaces are calculated for full vacuum. For the purposes of calculating the overall transmittance is useful to divide surfaces dispersants according to the stratigraphy or construction technology. The floor area is the sum of the functional areas of individual rooms, as measured at the net. The gross volume is calculated before closing boundary thermal zone air conditioning. The ratio S / V, under which follow interpolation to determine the corresponding value of the EP limit is the ratio between surface and dispersing Gross air-conditioned. Determination of the transmittance of the walls and the values \u200b\u200band Ug Uglim The calculation of the transmittance of opaque and transparent closures U can determine: • the values \u200b\u200breturned in the technical report if this ex-law 10/91 • according to the schedule delle strutture allegato alla Raccomandazione CTI R 03/3 Appendice A • mediante il calcolo secondo la norma UNI EN ISO 6946 “Componenti e elementi per edilizia - Resistenza termica e trasmittanza termica - Metodo di calcolo” conoscendo la stratigrafia delle chiusure opache e secondo la UNI EN ISO 10077-1 “Prestazione termica di finestre, porte e chiusure - Calcolo della trasmittanza termica - Metodo semplificato” per le chiusure trasparenti, e conoscendo le caratteristiche termofisiche dei prodotti o ricavandole dalla normativa UNI. La trasmittanza media globale propria dell’edificio si calcola secondo la formula: con S = area della superficie disperdente delimitante la zona termica U = valore della trasmittanza termica relativa alla dispersing surface. The transmittance of the building limit global average is calculated using the formula: S = surface area thermal dispersant delimiting the area A, lim = limit value of thermal transmittance dispersant on the surface as derived from Tables 2, 3 and 4 of Annex C of Legislative Decree 192/05. The correction factor is given by CCtrasm: Determination of the dimensionless correction factor for the plants to determine the correction factor on CCimp you need to know: • the useful thermal output power rating of the heater to service the building, by reading the label of ' equipment installed, the boiler or return value caldaia.Il Useful heating (η) refers to the value of Pn (kW) and expressed as a percentage • Useful heating efficiency is determined by the value of the boiler using the formula: = 90 + 2log ηlim logPn where Pn is the log 10 of the power Nominal working of the single generator. In the case where one PN generator greater than 400 kW shall apply the maximum value corresponding to 400 kW or 95.20%. From these values \u200b\u200bwe can obtain the correction coefficient value CCimp, according to the formula: Determination of energy performance for space heating (EP i, c) be assigned values \u200b\u200ball'edificioDai CCtrasm CCimp and determines the overall value of the coefficient correction building-system, given by: CCgl = CCtrasm CCimp • Next you need to calculate the index value for energy efficiency EPlim the table in Annex C, with interpolation based on S / V and levels day building of the resort. For interpolation we use the following procedure: • The table shows the values \u200b\u200bof degree days indicated as A, B, C and D the corresponding values \u200b\u200bfrom the table in Annex C kWh/m2/year GG1 and GG2, and the values \u200b\u200bof degree days limit of the climatic zone. The data are known the value of GGL degree days relative to the location the value of S / V. For the interpolation must occur before the interpolation between the GG to find values \u200b\u200bof X and Y, and after interpolation between X and Y to obtain the corresponding value according to the ratio S / V. This value is to be reported in the certificate of qualification energy. Once the value obtained by interpolation of EPlim you can determine the value of the energy performance of EPI, c using the formula: EPI, c = CCglob • EPI lim kWh/m2/year due in the building and report on 'Certificate of Qualification energy. To determine the value of primary energy for space heating can increase the value of EPI, c for the floor space.

Ward's Ap Biology Lab #8

DRINKING WATER ANALYSIS-BUILDING AND FIRE-PREVENTION wells





SI ESEGUONO ANALISI CHIMICHE DELL'ACQUA POTABILE

- CONTROLLO ACQUA -DEPOSITATA NEI SERBATOI CONDOMINIALI D.LGS. N. 31/2001 - D.LGS. N. 27/2002

- PISCINE VERIFICA UNI

- POZZI ARTESIANI E VIDEOISPEZIONI CON VIDEOCAMERA AD INFRAROSSI

Verifica la potabilità dell'acqua del pozzo. Assistenza per denuncia Pozzo

Email: caso.gianfranco@virgilio.it



Principali parametri delle acque potabili

Le sostanze che si trovano disciolte nell'acqua sono sali che provengono dal naturale processo di dissoluzione dei minerali costituenti le rocce ed i suoli attraversati dall'acqua di origine piovana. Quest'acqua è povera di sostanze disciolte ma posseide un'azione "aggressiva" a causa dell'anidride carbonica raccolta dall'aria.I sali sono presenti come particelle cariche sia positive che negative (ioni). La tipologia di sali presenti dipende dal tipo di roccia attraversata e dal tempo di contatto. Le rocce calcaree (marmo, dolomite ecc.) cedono ioni bicarbonato, calcio, magnesio; le rocce contenenti gesso (solfato di calcio) cedono oltre al calcio anche lo ione solfato; gli ioni sodio e cloruro possono invece provenire da rocce contenenti cloruro di sodio. In certi casi il contenuto salino rimane pressoché costante nel tempo per qualità e quantità ed è tipico di quell'acqua.Gli ioni presenti nell'acqua sono importanti per gli organismi viventi le cui cellule svolgono le varie funzioni perché sono immerse in soluzioni saline a concentrazione costante; i sali assunti con l'acqua contribuiscono a mantenerle nel giusto equilibrio. L'acqua potabile è una soluzione di ioni (ione calcio, ione sodio, ione bicarbonato ecc..) in concentrazione ottimale; L'acqua distillata ad esempio è da considerare non potabile perché priva di sali disciolti, lo stesso vale per l'acqua piovana o di fusione della neve.Ma quale è il quantitativo ideale degli ioni nell'acqua potabile? Già da molti anni ci sono studi in proposito che hanno stabilito queste quantità. Dal punto di vista legislativo è stato definito, per molte delle sostanze che possono essere presenti nell'acqua, un valore limite o una "soglia di concentrazione" che non deve essere superata; se in un'acqua sono presenti uno o più composti in quantità superiore al valore limite, essa non presenta più i requisiti di potabilità. La contaminazione di un'acqua può avere cause naturali o derivare dall'attività dell'uomo collegata ad insediamenti urbani, industriali o agricoli-zootecnici.


Principali contaminanti chimici inorganici
Lo ione ammonio (NH4+) deriva principalmente delle deiezioni umane o animali dove è contenuto assieme all'urea risultante dal metabolismo delle proteine. La sua presenza nelle acque, specialmente in quelle sotterranee, è dovuta in alcuni casi a cause geologiche quali ad esempio la degradazione di materiale in via di fossilizzazione (resti di piante, giacimenti di torba, ecc.). Queste acque, con ione ammonio che può raggiungere valori elevati (5 - 10 mg/litro) ma pure dal un punto di vista microbiologico, possono essere considerate potabili se non ci sono alterazioni di altri parametri. Al contrario la sua presenza associata ad analisi microbiologiche sfavorevoli costituisce un sicuro indice di inquinamento da scarichi fognari o zootecnici. L'Organizzazione Mondiale della Sanità e la legislazione vigente in altre nazioni non fissano no limit for this substance in drinking water because of its possible origin of "natural" and its negligible toxicity. But in Italy the law has introduced a limit value while classifying the ammonium ion among the "undesirable substances" and not among the "toxic substances".
Nitrite and nitrate can instead be produced in nature by oxidation of ammonium ion, or phenomena resulting from the use of nitrogen fertilizers in agriculture. The nitrate ion is in fact present as a component of highly soluble salts used as fertilizers, so it can move quickly into groundwater by leaching of agricultural soils. However, there are treatments for drinking water, technologically advanced and rather complex, for reducing the concentration of nitrites and nitrates until their total elimination.
The organoleptic characteristics (color, smell, taste and turbidity) of drinking water may be altered by natural substances. Groundwater is generally of poor and unable to keep dissolved oxygen, showing clear, iron and manganese in the form of "reduced" (ion "ferrous" and "manganous") even at concentrations exceeding the limit values. Underground water that contains iron and manganese in large quantities when it is brought to the surface is transformed in a short time (from minutes to several hours) in a solution turbid and yellowish looking uninviting. In practice, the contact with atmospheric oxygen changes the ionic form of these materials by "low" to "oxidized" (ion "ferric" and "manganite") and results in low solubility products. Thus we have the separation by precipitation of the yellow-colored slurry rust to black. Water with these characteristics do not present a health hazard, but it has undesirable features: an unpleasant metallic taste, can lead to corrosion of pipes and stain the laundry during washing. The aqueducts that draw water rich in iron and / or manganese have adequate facilities for the removal of these metalli.Un 'other substances of natural origin that frequently affect the quality drinking water can use the hydrogen sulfide (or hydrogen sulphide), a gas easily recognizable by the distinctive smell of rotten eggs. This substance is wrongly considered a sign of poor quality of drinking water are groundwater containing hydrogen sulfide very well from a microbiological point of view, and is known for many centuries, the therapeutic use of sulphurous water as drinks. The regulation of drinking water is expected that this substance is not present in ordinary drinking water because the odor is unpleasant and not recommended because it is taking for long periods. Hydrogen sulphide is easily removed for turbidity ossigenazione.La è un fattore che influenza frequentemente la qualità dell'acqua potabile: valori elevati possono essere dovuti a presenza di materiale argilloso oppure a idrossidi di ferro o alluminio, sostanze, queste ultime, usate nel processo di potabilizzazione delle acque superficiali e che possono erroneamente finire nella rete acquedottistica. Talvolta fenomeni di corrosione delle tubature danno luogo ad acque "rosse" per presenza di idrossido di ferro.
Tra i componenti inorganici che possono essere presenti nelle acque alcuni sono tossici: si tratta di quelli comunemente noti come "metalli pesanti" (cadmio, cromo, piombo, arsenico, mercurio, nichel, ecc.) pur rientrandovi anche elementi a basso peso atomico o che non manifestano proprietà tipicamente metalliche (arsenico e selenio).I metalli pesanti possono essere presenti in natura o derivare da attività umane. Mentre nel primo caso si trovano nelle rocce quasi sempre sotto forma di composti pochissimo solubili (ossidi, solfuri, ecc.), così che le acque circolanti solo raramente risultano contaminate da questi metalli, i metalli pesanti rilasciati nell'ambiente dalle attività umane non sono sempre in forma innocua. I metalli pesanti, data la loro tossicità, hanno una soglia di concentrazione ammessa molto bassa, generalmente dell'ordine dei microgrammi (milionesimi di grammo) per litro. Un metallo è tanto più tossico quanto più basso è il suo valore limite: talvolta è sufficiente una quantità small for any heavy metal to make water unfit for drinking: eg. are just 5 milligrams of cadmium per 1 cubic meter of water contamination, with the exception of copper and zinc than for their lower toxicity have higher limits.


Main
organic chemical contaminants include substances that can contaminate the waters there are numerous organic compounds. These are substances that contain carbon and which occur naturally but are also produced by human activity (the basis of the chemistry of plastics, wood, paper, petroleum and derivatives, solvents, paints). Scientific research continually invents di "nuovi" dalle proprietà tossicologiche sconosciute ed il cui destino, una volta immessi nell'ambiente, è incerto. Spesso si tratta di sostanze non degradabili o che impiegano tempi lunghissimi per decomporsi perché "sconosciute" ai microrganismi che operano la biodegradazione. Si ritiene che attualmente siano alcuni milioni le sostanze chimiche conosciute. Quelle effettivamente disponibili sul mercato sono circa 100.000 di cui circa 8000 tossiche e 200 ritenute cancerogene e sospette cancerogene; solo per 2100 prodotti sono stati individuati i rispettivi valori limite di tossicità. Ovviamente questi prodotti organici non sono tutti presenti contemporaneamente nell'ambiente: l'eventuale presenza in una zona è legato all'esistenza di industrie local production or use of individual products or product classes. Among the organic contaminants are found most frequently:
Trichloroethylene, Tetrachloroethylene and organohalogen compounds in general, the first two products are being used in laundries and in metal industries, water may also be encountered in other solvents (1,2 dichloropropane, methyl chloroform, etc. .) commonly used for degreasing mechanical parts.
hydrocarbons are components of gasoline and lubricating oils, spills of these substances in the soil can cause serious water pollution.
Aloformi (halogenated methane), and among these is the chloroform and other similar compounds. The presence of the aloformi drinking water (water systems) is not to be connected with the pollution of the territory: in most cases these substances are formed during some process of purification by chemical reaction of chlorine, used as a disinfectant, with natural organic substances of plant origin always in the water supply at the level of a few mg / L.


Main
microbiological contaminants are microorganisms (invisible to the naked eye) which, if ingested, can cause damage to the health of consumers. The diseases can be transmitted by water are quite numerous and are caused by various species of microorganisms (from largest to smallest): helminths, protozoa, fungi (mushrooms), bacteria and viruses. The most common pathogens in our climate are shown in the table below:
etiologic agents and diseases from ingestion of contaminated water
Classification
Pathology
Species
Helminths (worms)
Elminitiasi
Schistosoma (larva) Fasciola hepatic (larva) Taenia solium (eggs) Echinococcus (eggs)
Protozoa
amoebic dysentery
Entameba histolitica

Giardiasis Giardia intestinalis
Criptospridiosi
Cryptosporidium parvum

typhoid and paratyphoid bacteria Salmonella typhi and paratyphi
A and B +
Gastroenteritis
other Salmonella Shigella (various species) Yersinia enterocoliticaEscherichia coli (enteropathogenic) Campylobacter jejuni

Cholera Vibrio cholerae

Gastroenteritis Virus
AdenoirusEchovirusNorwalk virus

Hepatitis Hepatitis A, Hepatitis E
The drinking water in nature are increasingly rare, especially for microbiological contamination. Only the mountain springs, located in areas where human settlements are absent, can provide good security guarantees, but already the presence of wild animals can lead to phenomena of contamination of acque.E 'therefore not advisable to drink water because uncontrolled requirements do not apply as the purity, freshness and the isolation of the area to ensure the absence of risk. Even the water of deep wells, which should be better protected from pollution, does not always offer guarantee of purity, therefore, should be regularly monitored and appropriate use of drinking water treatment.


type of analysis recommended
A water can be declared fit for use only when drinking was analyzed from both the chemical and microbiological: no claim (the absence of turbidity, the sense of pleasantness, environmental isolation of the course or water source) is a sufficient reason to declare water "good" or risk-free. For the water distributed by waterworks the type of analytical control and frequency legge.Per supplies are dictated by the private, established that the uptake works have been made in a workmanlike manner, you should type bacteriological analysis. If this has a favorable outcome can be carried out chemical analysis of the basis for characterizing the type of water that used to be. If necessary, specific contaminants are to be sought in relation to environmental conditions: the presence of industry, agriculture ecc.Se the bacteriological examination yielded negative or you leave the resource or the chemical tests are also implemented to better decide on treatment of drinking water to run .

Best Putters Under $100

RADIOACTIVE CONTAMINATION CHECK


ACCEPTED FOR APPOINTMENT OF FIRE PREVENTION PRACTICES

LIST OF PROFESSIONAL WRITING AT THE INTERIOR MINISTRY -
LAW NO 818/84 BY REQUEST 1986

cost estimates

Excellent knowledge of Active Matter '91 - 92 - 94-DM 16.02.1982

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ARE AVAILABLE FOR INSPECTION BY RADIOACTIVE CONTAMINATION SENSITIVE GEIGER COUNTER - Radiation: ALPHA BETA GAMMA