PT106692A - COMPUTER METHOD OF ASSESSING THE QUALITY OF THE URBAN WASTE COLLECTION SERVICE - Google Patents

Abstract

THE PROPOSED PERFORMANCE ASSESSMENT (MAD) COMPUTER METHOD IS FOCUSED ON THE EVALUATION OF THE SERVICE QUALITY OF THE DEPOSITION AND COLLECTION OF INDIFFERENTIAL AND RECYCLABLE URBAN WASTE. THIS METHOD APPLIES TO SEVERAL CYCLES OF EVALUATION OF OPERATIONAL AND ENVIRONMENTAL PERFORMANCE OF THE MANAGEMENT AND CONSTITUTES AS A MODEL OF INFORMATION ORGANIZATION. MAD IS SUPPORTED BY AN ARTICULATED SYSTEM OF PERFORMANCE INDICATORS (SID) THAT GIVES YOU THE ABILITY TO EVALUATE THE OPERATIONAL, ENVIRONMENTAL AND ECONOMIC PERFORMANCE OF DIFFERENT MANAGEMENT OPTIONS SIMULTANEOUSLY OR AUTONOMY. THE ENVIRONMENTAL PERFORMANCE EVALUATION REWARD PERFORMANCE INDICATORS (OPERATIONAL INFORMATION) AND PARTIALLY ADOPTS THE ENVIRONMENTAL IMPACT ASSESSMENT METHODS OF LIFE CYCLE ANALYSIS, CML-2001 AND ECOINDICATOR99. ANALYSIS OF MAD RESULTS ENABLED THE VERIFICATION OF SERVICE LEVELS, THEIR MONITORING AND THE CREATION OF BENCHMARKING ROUTINES.

Description

Computer Science Method of the Résiduos Tírbanon

Technical Domain of the Region of Urban Affairs; performance appraisal; Avadiaçao / odrieniai and Analysis of Cycle of D ida. Scope of the invention Evaluation of Performance of Systems of: Collection of Uctan Waste

As part of its' research and development activity: at the University of Trás-os-Bontes and Alto Douro, the team responsible for the present patent application has been developing, since 2001, research on the performance evaluation economic, and environmental impact of urban waste.

The Evaluation Nodes of i) are operational commitment and implementation are supported by performance indicator systems. These indicators are public monitor shoes? · And psivados > to evaluate the components of the management of the systems (deposition, collection, nvanaxerenoia, transport, transport, and transportation), to assist in the development of technical and demonstration aids and decision-making inatrnmapios. The UTaD already unveiled?:? 4 performance indieadovee eisteaas, Dole systems resuitara? $? of the adoption and adequacy of the proposed audits by Morms ISO li 032002 and by the Model of the Civil Engineering Laporator. From the Performance Assessment Model for the Hordestu's Inventory Management System and the Model 4 Performance Assessment of Recyclable Material Design Systems, Seawol. and adapted to the needs of waste management systems.

Have you had any serious problems before your child in the performance evaluation? Management of urban wasteland: te ?. as well as to support the analysis of the Life Cycle, in a blatant context, the team there developed animental evaluation models for the EIM, in the case of the study of Si. s tems Interma? ' ricípal. of the besteo dg

The development of these ptojeofcos allowed to identify difieuldadet and licitagdes in the application of the evaluation of performance of the soils of urns, name ad ame nts: a) the absence of .nm: ; • The first difficulty lies in the fact that, in the case of the national authorities, there is a need to ensure that there is sufficient information about the operation of the basic applications. integrated analysis / evaluation of the value of waste, Another difficulty and the need to affect human resources and wastewater management, as this applies the diversion of operational and operational resources.

The limitation of these models is- "color; the reduced agility in the availability of the rash, the smaller the greater the temporal reference road of the model. Models with a large number of indicators require the processing of considerable base data, using mathematical operations, to obtain the calculation variables. This feature will contain information on the calculation process and the disclosure of the value of the indicators.

Another limitation * especially in the models with network analysis periods, by daily basis or to emanals, is the high human-to-financial effort in the processing of information, which involv- es its application to management entities under the terms of 1 1 in ance 1 ros. The answer: the limitations and difficulties in the implementation of performance evaluation systems is the fraction of the calculation of the indicators. This option allows for the creation of evaluation routines, for the improvement of the quality of production, for the elaboration and evaluation of the producers and for the creation of histories, the weak linkages of the production of food, and the emergence of complicity in the use of informatic tools: its acquisition and maintenance, and the specialization / utilization and resources of this activity. The success of this process is based on the success of the evaluation process, the development of procedures for solving, validating and costing the quality of basic information and calculating variables. the recommended temporal and geographic reference units are the year s area of intervention d a e n t i d a. from e e s t The main limitation lies in the fact that it is difficult to manage the high level of risk capital required (in the time and space of the various types and groups of indicators). Another weakness is the difficulty of adapting the components of the applications the characteristics of the systems, in particular, the collection, transfer of waste and the management of waste, the evaluation of the technical, economic and environmental performance of waste management requires the development of a model for the evaluation of the performance of waste collection which simultaneously integrates the environmental economic and operational components, supported by a single, simple ID (not the corresponding composite), to the combination of elementary variables (calculation variance).

The traditional models of the operational performance model and systems of Sestao de Residuos Urbanos (SGRUl) are characterized by their ability to analyze and analyze the operational, economic and environmental results. performance, supported by performance indicators (ÍID) f are fine inc. ip.ienr.es and rest.rotimos in the production of information that enables the integrated evaluation of operational, economic and environmental performance.

Another feature is the high complexity of operation and reduced id.exiblity and adaptation of operating methodologies to regional realities different from its matrix: zsferencria. Some existing models may be categorized as "black boxes" once the user has only finished: the introduction of predefined information is allowed and the results are received, whose plague and validation is impossible. Another factor is the excessive simulation of the modules. dedicated to the evaluation of the operational, economic and environmental performance of the management components " of urban waste, including collection and urban cleaning.

Although no model of performance evaluation can be classified as good or bad in the evaluation of systems, its adoption should be geared to the territorial scope. and the components of management that integrate management systems.

This reality motivated the development of a Performance Evaluation Media: diAD) for OGoU that simultaneously contemplates two versions. the operational / economic performance appraisal of the environmental performance, supported by a set of Performance Indicators. The TMAD Performance Measurement Model (TMAD) focuses on the components, waste management on disposal, collection and collection, iodafereaai.ada, a. disposal and selective collection of recyclables and urban cleanup. It was air. Models applicable to various purposes, for example, in the comparison of the performance (operational, economic and environmental) of the main operations; management of resldues; in the quantification of environmental impacts; in the optimization of Models and options of management and in the management of information relative to levels of service, supported by external entities. The performance model (MAD) developed focuses on the disposal and undifferentiated, and selective collection of urban waste and urban waste in order to compare and perform (operational, economic and environmental) the management and management components, the quantification of infrastructure and the environment, and the selection and / or opt-out of the best management options, and systematically and informally on the service levels of the management entities-> It evaluates the operational and environmental performance of the managerial entities simultaneously, and it stimulates external management routines (between management and internal entities (between do- ments, departments, departments and teams). operational) and assures the basic needs for service assessment and monitoring. HAND also constitutes a model of the information organization once which allows the histories of results of several assessment cycles, enables the definition and continuous improvement measures either in the management components evaluated, individually or in the management entity, as an organization, the result of the indicators allows the self control activities management and a common operational constraints and the planning and definition of sectoral policies.

Authors like Weitz ei ai < (1992), Vidai et al. (2001), Iglesias et al., (2003 ;, et al., (2005), Moberg et al., (20), Bovcu * Poreii (2006) and Bânar et al , (2000) recommend that in the decision-making process (in the design of waste management systems) the environmental assessment should be complemented with economic and social indicators, the proposed design suits the complexity of the Brbano Waste Management Systems (ORO), responding to the need of its Managing Entities (EoE) to monitor and evaluate the performance of the various operations integrated from an operational, economic and environmental point of view. In addition, it assesses the economic and environmental emer- gencies of decisions and makes feasible the use of environmental aspects or indicators, such as criteria for merit scoring: environmentally friendly, with goals or objectives # of proposals and public tenders for boreholes management services, model And AP and to any time period clearly defined, D is especially intended to be applied in a geographic unit such as the area of intervention of the SlR11 as long as the unit and the year from the scope of this Model are excluded from the components of landfill and maternal recycling, and organic anaerobic ingestion and 100.poet: agesd incineration and transient transport ir. In addition, hazardous wastes from industrial residues (Panels and dangers of residues (Bosporus 111 and IV) and special waste: residues (waste oils # vehicles in ΐΐ of life # used tires # accumulators # batteries and sludge and STári,

This evaluation model is supported by an articulated system of indicators of economic growth (it is possible to evaluate the economic and environmental operational management of urban real estate) (figure 1). G S1D can be used antoxiornamente in the evaluation of operational and economic performance of the EGS, V integer analysis of the IDs and the performance evaluation # the verification of service levels # the monitoring of operators # and defines internal and internal operating routines and The evaluation and evaluation of the life cycle analysis (AIACV), The scope and objectives of the evaluation of the MAC must have stipulated the assignment of the cycle This is due to the fact that, in case of damage, it is necessary to identify the services to be evaluated, to assess the environmental impacts to be quantified and to 1D that will support this evaluation (Figure 2 ··· Conceptual Model of the Performance Evaluation Model) "well all TDs that integrate; the MAD are required for the purpose of the environmental performance assessment, only those required to qualify for the selected impact categories < The performance evaluation requires dl Sponibi! The methodology CML-1001 provides an assessment of the environmental effects of the local, regional and global level, and is based on the calculation of the environmental impact through the partial adoption of the CMM " through the calculation of impact categories, The inclusion of Eco-ii-cabor92, nm Environmental index that relates the impacts to the environment, has. and to compare the environmental damage caused by a single numerical value, MA D quantifies the environmental impacts of the management of urban waste in municipalities, systems and management of waste for, for example, climate change, entrophication or forest degradation, and develop relative environmental performance scenarios; • The implementation of policies and management strategy.

Another relevant e-commerce is its simplicity, in such a way that it can be supported by a specific computer application, which is discontinued, in the form of Ercei 1003%, only with the effect that some fields for introduction management of information. This crater is roulette since it allows it to be easily adapted to the realities and milestones of waste collection or urban cleaning.

In summary, the MED is an information organization model that refers to the municipal waste management services that present quality dynamics, · to alert, for situations that are undesirable in terms of non-compliance with aspects of quality, service provided. said, is able to translate the political and administrative reality of urban waste management to facilitate the comparison of the performance of managing entities to operate in. as a consequence of its capacity to systematize and contextualize the responses to the requests of the entities involved in the supervision, regulation and regulation of the sector. < / RTI > performance evaluation and supported by performance indicators to quantify 'waste management' operations. However, the fact that the error cm. sponz zz m zsda, for this enumeration of indicators, it is possible to be analyzed comparatively, and it is possible to interpret them for different ages. Indi tors have to be organized, grouped and contextualised. D is suf fi ciently flexible and robust to assess performance at various levels of responsibility, 1 age from EGS administration to those responsible for operating services,

This option allows the collection, trans- ference / transport of waste and the 1 impera urbara to be observed, the use of SID also avoids the loss of information; the calculation variables and Indicators} resulting from the aggregation process, especially for the external users of the 1 st module. The definition and definition of the 10 take place in two strands, One. which looks for indicators that report on the status, facilities and equipment specifications, another that looks for indicators capable of analyzing technical and operational performance and for integrating information on the obpects! management and control constraints, regulatory, technical, technological and financial constraints.

An important requirement of SID is the use of a reduced but feasible number of indicators, so in the design of SID it favors indicators that are representative of the political and regional context of waste management and of the operational, technical and economic performance of management entities, In this way, the screening and selection of the evaluation should take into account requirements for each indicator, indi- vidually,

Yes

The IDs to integrate will be hard. 1. Iment and Acceptance by indepen dent entities, and that your site is free of charge. g n i f i. ca t i. and the overall efficiency of the operators. It is the same as in the previous example. It is another criterion that its measurement is of the highest possible quality, and it is the object of the collection of the basic information required at the time. and impartial in such a way as to exert prejudicial or distorted judgments < and consistency, articulation and fiiexibility of the CIO should be verified through. adoption of three requirements; i; exclusion of I.D from difficult to unrealizable. and the inclusion of 1D canas is to represent the most relevant aspects of the deserrper of the ECrr) to refer the system to a defined period of time (nm is the year although in some cases other temporal units may be used) and to a geographical area, well delimited and coincident with the area of intervention of the GSO; (iii) absence of a substitution in meaning or objective between indicators and their applicability to EDS with varying degrees of development. The two types of information: Information on the Profile of hrrtisiade eestorSv fedGbx) and the System Components (Tapeia 1)

Group of Indicators

I7 &amp; tax &amp; PEG í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í í d. Ϊ Ϊ Ϊ Ϊ Ϊ Ϊ B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B. B.. Indicates Ecofelaic

Collection Selecv. xva of RecyclablesfHSExx.)

InformationCo π t o x t. / Enq uacr ame nt. the Bv Operational Performance Indexes, 1 Eco-nomic Importers L Impes a Urda naCLCxxt. B. Performance Indicators Operational Information on the Profile of the Management Entity is indispensable for a proper interpretation of the corrections to be made. ipending on the budget: 1 bag of the internal SGPU in search. This description describes the geographic impact of the operation, the type of property, the dating of the employees, the rates practiced, the investments made, among others, the ISS. This discussion is only to be translated from the basic indicators or information (calculation variables) that frame, and define the EGS and the. region, among other aspects, describes the geographical area; of action and suo. urban occupancy ', its obtaining of transport supported by and to official services (for example, population served, number of fires and population density; or data obtained from the inventories of the EPS (for example, the love of the vehicles, number of traffic violations and support infrastructures), Ά Information on the management of the BE RE quantifies the BGKE mapping or integrates the the main components of management in the balsa · '' ', name, the Undifferentiated Collection (Eira), the Recyclable Collection (RSRs) and the Limpera urban iifJss) * This information is provided by Indicators of Contast Information / Framework; X Performance Indicator

Economic Indicators or Economic Indicators. The Group of Information Indicators of the Government of the State of Rio Grande do Sul discusses the performance indicators of the management components of the ERMS, describes the state and characteristics of the installations and the equipment to which each component enables the feasibility of comparing the soo performance with other EGE! In the case of slave beavers, which are independent of gear options (by contrast, the amount of waste processed or the number of inhabitants served), and whether response factors or returns depend on the options available. of the medium-long-term management, the number of entities or the typology of con trol. The group of indicators Operational Performance describes the operational know-how of the SGlP in relation to the use of resources in the field (such as turnover, tonnage distances, and collection rates). These markers assess the productivity and service levels of the EGS, analyze the amount of work and efficiency of the tasks performed by the workers and describe the duality patterns of the service delivery through the treatment of response times to requests and reassessments. the operational performance of the undifferentiated collection and the selective collection of recyclables make it possible to characterize the operations of deposition, collection and transfer and transport of waste according to the topologies (in isogues) of waste deposition and deposition equipment (shut-off and individual) ; In the case of the indicators of the performance of the urban area, these factors are the operations of sweeping and cleaning the streets. The group of economic indicators expresses, from the financial and economic point of view, These indicators are intended to be used for planning: economic and cost control and cut-offs and to translate the overall cost of services and components of undifferentiated collection. implementation of a collection methodology, it is financial information based on de fi nition. lion of cost centers {deapeaee gerai et echelon of eercuioe; eeiouioet macereaçao coesomo of the fuel; charges and taxes; Installations of sereiçoe to support the calculation of idlers, d The indioadores of economic performance of the undifferentiated collection and collection, deseectiva. are indicators relating to chasms with deposition operations. »collection, transfer and transportation of. For the purpose of this, the costs are determined by reference to the flows and loads collected and transported and the methodology of deposition and collection of the waste adapted; h The economic indicators of the orhana cleaner characterize the operations of sweeping and washing streets,

Holding the HAb to define a 51D is not obligatory that the EPS o / 5 d np make the Integrate or not that they may not need all the groups of indicators: proposed »In this way; groups and ID numbers depends on the needs and territorial and territorial development of the ESS and on the availability of resources and data resources. (human and veterinary) to remove the studies with the appropriate rigor and detailed information, it is recommended only the inventory of operations, emissions, emissions, or energy contamination should be recorded and / or inaccuracies should be noted and of the knowledge of all those involved in the process of treatment. Each physician should be associated with a rigorous definition, with the attribution of a concise summary, and the terprecision and seclusion. involves the set of calculation vectors, determined from the case information. These variables of calculation are included in the concept associated with each of the indicators. calculations can be generated externally (external data) or generated and controlled directly by EES (internal data). taking account of the ioc alities. s vasotes obliges

To ensure that BGS can control which of the information age the number of indicators calculated from external data should be minimal: For example, IPs: whose reference variable is the resident population should: if the population is the phenomenon of daily migration, the difficulty in obtaining is to adopt the population values available in the national,

In order to collect the basic data by means of the calculation of the indicators it is important to check their consistency by comparing it to each other and, if this is the case, with the data, its achievement should be adopted: for example, the following standards of quairdaoe :

iB

Accuracy - Measurement of the variability of data values for each class (ea &gt; cedia, standard deviations: -; - Qualitative analysis that assesses the qualitative analysis of the level of the doe reflecting the reality of the SGHU. until it reaches me all Idea: the technical data from here to the aedo of the data is applied from the anifonzze force to the various processes and operations in state; 1 &quot; Reproducibility qualitative analysis that evaluates: which to: sz'ztor.zzisçao on azezrodoropiu o The data used allows entities to erroneous their reproduction.

(.10) should be typically expressed as a ratio between caries, cane or adventitious (by ca (%) or caries), they ask the child to express intensity: a. to n &quot;; km, and n &quot; 1 eh, to a &quot; d, The conditioner t of color will respond to the rule of the procedure which specifies its calorie formula the unit in which it must The information provided by the Management Entity contains detailed information on the basis of the information provided in this report. Although the population is expressed in terms of variance according to the definition of the indicator of the disease, the population served or the area of influence of the disease is not included in this study. The purpose of this report is to establish the basis for the evaluation reports of Ceseopenho the interpretation of operational information by the users of the results, most of the X: D crazy aspects related to the data; the operations of management or the rendering of service, Some IDs are &quot; neutral &quot;,ie; represent indicators that are not under the direct control of the management entity, although they provide information relevant to the function and perception of the levels of service provided ... The proposed S1D Integrates its dependent IDs into one another, which, in its conception: it is feasible to exclude the IDs that are passed on from others. One example is the indicator of the productive speed of collection, which is a function of the effective distance and top indicators of collection ;, However, the advantages of its use performance assessments recommend integration.

In the Mistake! The origin of the reference was not found, it was defined the calculation variables related to the management system that support the definition of NAD IDs.

The following lists include the selected Indicators and allow, in a complete and complete way, to identify each ID, to know the unit in which it is expressed and the explanation of the associated description / description. K each indicator was troubled a code, according to the group of iudiaedares a. which belongs. 2 ~ List of Measurements to a Measurement Amount of

support for the IDs of the calculation of the Calculation of the abbrevation of the containers (Rind, Roe, and km * Capacity of the installed capacity of Ro, Distance from the city of km. Distance from the urban area (1 km) Distance from the collection km Distance from the road km (km) Distance from the urban area (km 1) D uring or p arating: a va rs of containers with t Hurserd of utility contracts; D eter of eco-centers and co rdro ules and the number of buildings ed ered to the tops of fire. Tubi l of Untes serve dúresro ha.d infraççdes of the strip rr i trârdrto Dtoexo intervrnçees of the hip nanou o disinfection: the rotor eonteniorea ddoer the reciunagries rociar; dèrrioro workers full teopo rat t d ass 1 c ro ve rr 1 ro ve ha p.reo Amount of RCi and Rur collected too

Container bags semi-entrapped bag Cargo time of containers per minute or seconds; Container loading and operating time at the pick-up point after the vehicles have been unloaded, and K: at collection time, and the transport time (hours; h Transport of water and sewage Water volume l cu af Volume of gas oil Li or o: '' .4. Profile of Sst age Manager (PBGrs) go

Ttíúx & M.úòr Description Units FEGj Identificegae Ge. EGe (Municipality, Service or Company) (-) FSGi EGEU Identification (Moe of the Waste Management Diagram PE) pm3 EGS Headquarters (Locks r4) pm4 limtoi. (G) * Service coverage rate (Number of fires served by the BGRU / Total number of fires (*) Number of fires served by BGRU / Total number of fires in the region) x 1.Θ0 Hd PEGy Gt11 service providers (Number of service use contracts) {contract OS} Code

Indicator

description

Sn PEG age &lt; Intervention area of the district (km ') SEÔ' Population of the United States of America (Ρορκ laçã ·: · rsrrdsnce in the sfbdl Intervention Area / Residual Residual Residual / Total Mineral Wells ("hab") »» »Number of fires per building fdámero of fires / darsro of Pieces of buildings 1, Population of population living in the area of influence of the SGst Population distribution of the population in the set of population: Growth rate: of the population f (FopulaçPx) residing in the spatial area of the spatial distribution of the resident population, / .Population resident in the previous year) x 1o (%) P1G? 5. Full-time employees dVanero de Busco Full-time employees at EGSà (Table 1), the number of workers by type of service (Total number of workers at the end of each type of service / Total number of workers, ) E e e e e e e e e e e e e e e e e e e e e e e e e e e e e). The average service time of the service providers is: (a) no, if i (c) (c) (c) (c)

Indicator

unity

(1) (1) (1) (1) (1) (1) (1) (1) (1) (2) Accidents of road transport accidents (Quantity of RU processed per os) (Annual quantity of processed goods per year) Quantity of RU processed per os (Annual quantity of processed goods per year) Rd processed in the same period of time) (ko &lt; hab Pdia &quot; ') FEG;?:; Annual Expenditure Expenditure (Gaussian Expenses, Expenses , Annual expenditure on the disposal of waste, the costs of production and the costs of production, installations, year of production, annual operating income and annual expenditure. services provided by: (€, an o &quot; 15 PEG; € 5 Annual allowance 1 (equalization and infra-structure) the acquisition of new vehicles and the acquisition or renewal of facilities, etc.) (£. &gt; year &quot;! &quot; &quot; &quot; &quot; (Unit cost of the RUi imiination) (idtorCC 24 Code)

PBG.Sity indicator? Annual basket. of the oxidation eluate is obtained by thickening the surface with the elimination of Râ,ƒâ,,â, ... PEG; &gt; R a t o o o c o c t t. (for the purposes of the present invention, the invention relates to a process for the preparation of a compound of formula (I). How are you? of the dCM? / center of the center if \ k.? *; '? &quot;. I echo you m and of the: age of ecocent rea: residing feopoiag / eco- fh.ah, echo o &quot; d

id InfQzm &amp; çMu About the SUGU Management Performance

Collection of data, in accordance with the invention, in accordance with the invention, in accordance with the invention, in accordance with the accompanying drawings, in which it is set forth in the accompanying drawings. GUI guidewire (s) (i.e. 10 '· g' '' '' '' '' '' '' '' '' '' '' '' '' ' (a) and (b), (b) and (b) (b) and (b) (b). : 1) Ability to traesfarência eaiada sOS (CEP ACI d im dc would t rad s teténeía of Ruil íbdb diet ~} Code Doscriçâo display unit KXA 5 Workers afestos the collection, indiréranelada (t \ iUZã &amp;.. £ Ú · CtB (1) and (b), and (b) the amount of RXA, is the distribution of the traffickers by reason of the collection of indifferentia of the full-time labor force per type of day-to-day activities of workers in the labor force at 1100 hours. Total quantity of RU collected: (total amount of RUi harvested) (total) of the total age of Rhi collected per day. 365 days) J {kg, hab: &quot; 1. day &quot; d RXa.5 Dioxylation of residues (Q ue a t i of total RUi collected by type of deposition and collection / Total amount of RUi collected); IMG RXã. The quantity of RUi collected in the year and the year of the collection of the previous year) / Quantity of RUi collected at the rim and at the end of 100, ··. tJ »ád & db • Indicator Indicator Dosing S &amp; i o o o hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab hab i i i i i i i i i i i i i i i i i i i i i. haiMb ** at the Oepoo's capacity as the per capita capacity of the tonnage capacity of the tonnage of the tonnage (tonne). 3 Collection effort (total dioxide of the type) D & E / Deposits / Total Daily Disposal of Waste Water and Wastewater Disposal Waste Disposal Waste Disposal Waste Disposal Waste Disposal Waste Disposal Waste Disposal Waste Disposal The reaction mixture was cooled to -78 ° C. The residue was purified by flash chromatography on silica gel, eluting with EtOAc, dried (MgSO 4) and evaporated to dryness. (kg) in the period from 1 January to 1 January 1990, the total number of days in which the total number of days in the calendar year shall be calculated. B. &lt; RTI ID = 0.0 &gt; &lt; / RTI &gt;

(Electricity / Electric Power Consumption / Electric Power Consumption / Electric Power Consumption / Electric Power Consumption / Electric Power Consumption / Electric Power Consumption) difoeohexadecyclohexylcarbodiimide hydrochloride. reooidide / {fresh. KdtcrT d 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0. s. 4 Complaints of the service with satisfactory resolution (number of complaints with satisfaction and satisfaction / Number of complaints) lõõ (i .; * * * Term of service and service measures (Time for resolution of the complaint The number of containers collected by the erection distance (number of co-cocrores / collection of waste) (cont'd) (cont. .km &quot; &quot;)

Indescribable Code description Unit RI®,;? (collection of waste collected by telemetry dr spooisel (total waste water capacity) / Total capacity of waste disposal by waste water (also in RX). * Distance traveled by COn t sát or 1: · va do (Distance from io magem &lt; € CO: s rowers / doe and the tear t er es i (km ooent) :) Rto.s time ca lasoqem by (cont'd) (cont'd) d% Z *, w CPnomotion of the container in the 1st row of the container (s) of the container / number of containers i (cont'd) In the present invention, the composition of the compound of formula (I) of the compound of formula (I) of the compound of formula (I) may be prepared by the compound of formula (I): (1) and (2) and (2), and (2) and (2) are as defined in claim 1, ; Hygiene, container processing (the term of the letter of the special service) and the name of the recipient (s) of the core group (s) Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο. ] HXr &lt;, j.5 Noise of the indirect collection (at the collection point during the harvesting period) Total net collection (per tonne of collected tonne) Distance to the collection of the collection / Quax: collection age (Rn, · t or '') RXs. The collection effect per tonne collected (Drying distance from 3d to (total time of collection per tonne collected (7ex; .pa total of collection of the circuit / qui city of ICi recei.hi). (collecting tonnage per tonne collected) / Body: collecting the waste from the collection to the collection / recycling bin) gr Indicator Description 'tínidad®

Conab of coabusr. ive i pcr the half-life of the circuit collected; / B (M-collection) number of (x) (i) BX ', and P r odu t1 v. 1 of the cc. have been collected. of FUI reco Ihida / /'.duo oro de t ratai na dd.ree .0 torípo · integrated collection clean: of the eianuui roi / los., t rab &quot; dc &quot; (b) Total velocity of collector's collection / total velocity of circuit (hr) Circuit or speed of recov- iàtodj; kto h &quot; :) XZx.M vo.i. (see, for example, the contents of the carton) (see, for example, the contents of the carton). (a) The unit capacity of the unit and the collection point / collecting point (s) of the collection point (s) ) g g »» »» »» »» »» »» »» »» Código Código Código Código Código Código Código Código Código Código Código Código Código Código Código Código Código Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Ο Water consumption and eco-centers (Water consumption and water consumption) ('Water consumption' and 'Water consumption'). Volume of water / waste quaity} e / C too &quot; 1} ΕΧβ, χϊ? Distance of transport of fairies and fairies (distance of transport of floras and .fileiras / and time limits for the transfer of strings and f Time of transport of plains and rows / Quantity of PJ. (fuel consumption in the transport of flows and fuels / Quantity of fl uxes and transported taxes / tonnage). In the case of transport, 1 of 3 [> Piece Quantity: The Effective Translocations / (Mutual of Trafficking 1 Donors at a Time of Transport of 1 to 1 Rows)] (ron. (B) Bconomic Indicators

Indicator I &gt; aa &lt; tb &gt; RI and COCOOCO of the ROCIO INDIA. year 1 a; (-;; .0 C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C (quantity) PDeepeaas da d rd / Csaat, age: total of additio ng / Management and WcQC & mmm s * g% The costs of the eco-coding process and the transport of x'iodo.a; tximximate / dexterity of the deceased. (1, 2, 3, 4, 5, 6, 6, 7, 8, 9, 10, 10, and 10). (Number of Freight Vehicles / Quantity of RUr taken) (vaio v 1 Gborf5; RSR, = Service time of the vehicles (average service time of the vehicles to the frei) ianos. vaio &quot; 1) RSR5. 5 Ropulation served by selective collection vehicles CPqpnlation served / Number of brake boosters. (1) (4) (4) (4) (4) (4) (4). lb &quot; ton ~ i} RSR. 5 Discretion of fc raba i. (number of full-time workers by type of training), the number of full-time trainees, and the number of full-time trainees in the mid- The reaction mixture was stirred at room temperature for 1 hour and then cooled to room temperature.

Code Ittdieadctr Bescriçao CPaidada rove π r P i I o ci ce reetdnoe (Q water nti given totai copy Jidr reccdh.nio RIPO by deposition and dlleira / Q en u c ICIA the tota I of Ror collected π} 100 (KSI Pd The annual rate of collection of the collected data for the current year is shown in the following table: Year-on-year change in the year of collection Year-on-year value in the previous year: * Rate of collection of recyclables (Firefalls served by Roei / Number of fire ri κ 10 o% 1 Per capita deposition capacity per haoitanta (Total capacity of air containers per type of shipment / Paper o (s) of the sample (s) of the sample (s) of the sample (s) served by the sample (s) deroe of the East and West, and the rate of deviance (ζκοιο effluent / Total amount of RU collected} r Ιϋϋ \ ^}

Unit T · VV- »tV-> (b), (b) and (b) and (b) are as defined in claim 1, wherein R 1 and R 2 are as defined above. ) S.SEA, J5 Efficiency of Dos7 1.0 (Deviation Τάχα / Tu xá po ler · oiai desvie) x Tõõ í%} &gt; f &gt; Β, m ommcmmL · Céãi $ ® Indicator Daacriyã

Ssubject C Gsrax, &gt; the Corsica de en e r g i a e 1 is c; t ri. and the support for the support of local and regional aid. of da (s) of the salt of the salt stream (Number of lines of salt), and the number of salt per cubic meter (s). (number of repo- sations per type aa to et al.) / Remainder of the revo- lution (a) - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - a) RSRg, 5 ................................. Terripo - resonance frequency ie the 1 part of the (average time of collection, number of complaints), number of days of collection, number of days of collection, number of days of collection, ................................................. { Isoperophenylacetic Acids (Oopo-rites) / Occurrence Date of Occurrence of Occurrence. (Total number of containers (ecopoints ;;) Total number of containers (ecopoints ;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;;; (collectively, the sampling point at the sampling point), and the sampling station at 5 meters / (dB). ) Total amount of waste collected by epoetheteric wastewater (Quan ti Nade t ota 1 of RUz collected / Total capacity of disposal of waste water users): Collection of wastes RSRb.k Distance (collecting distance from the 1st to the last point of collection of the collected tonne (Distance from collecting from the 1st to the last point of collection). collection time (km. too) B.8Ss 12 Total collection time per ton collected (Time of collection: recyclable water / Collected waste water) • b, toe &quot; 1 RSR &lt; / RTI &gt; Actual collection time per tonne collected (Collection time from the le to the expert collecting circuit / Quantity of rUr collected.) (H "tón ~ J '; Code Xndrcador llaxdad®

Censure :; of the amount of collected oil (Gasoline Vol.) collected from the P0. P: CO0 PO: / disease of the recovered compound, Cl, too. 1 - Ratio assignment: re-routing of the tag to the address of the tagrai; , 8, 8, 10, 12, 12, 12, 13, 13, 13, 13, 13, 13, 13, 13, 13, 13, 13, the total cost of the operation of the pceporrtoa at the point of j / Capacity: The total cost of the operation of the pceporrtoa at the point of j / Capacity: t eco lh aja: n ote of the tecppodto} | eor toateerec do j eocpoetoj {seg οΡρ;

C. 3αOXCA, ORSS & CONOHXCOC

Codrgo Indicator Usordade Escorar. SsJaSCTXVA RSEc. Calculus of the title compound is 0.1: 0.01. 30% of total donation / $ 0 to go! duet of the recycling of old age; (Deepeeee de Psol / adora ti of the Bddr da.

D, ISfOKMAÇÃO DS CONTEXT / SNOUAbSAMENTO Code Posscrição Indicator Unit Χ &amp; ΧΛ Humero cie reicolos urban lixapera LU / Λr and the intercexxçao) írale v km. &Quot; *} · l &amp; H.2 Texspo of serripo of vaiouLos (average time (years of service) (%) Population served: per vehicle of 1 i urban opera (Popaia saroi da / barero of LU vehicles) hafc, re i ο "" Rate " of urban coverage (Intervention Area / Area of Expenditure x 1) IOA, .5. Workers in urban areas: (Number of persons employed in urban areas in the LU / Region of employment) (km.) "DX str í fe ui za tion of workers by type of Ximpera activity, urban (Number of workers at full length by type of LU activity / Number of full time workers at LCI) LCa. (total quantity of x ox reooj, in the Vmec group) (log year "&quot;).

Eu PB Dese & psnko Opsracxok ^ i. Cédâ &lt; jo Indicator Description Ucidad®

A solution of the title compound as a white powder. and i is here below. will be charged for the cleaning fee / cleaning fee. , to 'a: 1¾. z ceclamaçaies of:. seroiço (Bãmero of reciaaraedea / rofcervencãoj area (roo i on km &quot; '.} IIOP j Complaints SOXVV Λ - ^ -' Ο Oiaoi reaolagao Sís ti s £ lands (reclamaodee number of color recci APAO service and the tiara t dr ia / Meara de la Pataa, and the average length of the reopening of the reola. (1) Mls.s Origins of rare occurrence in relation to the number of species by type of nesting / Number of re-nesting (s) Scanning Productivity Manua 1 [V / V Distortion / (Variant): Time-Lapse Time-to-Time Vibration Time VARRSPam M &amp; Pneumococcus pneumoniae / Pseudomonas pseudomonas, Pseudomonas aeruginosa, Pseudomonas aeruginosa, Pseudomonas aeruginosa, Pseudomonas aeruginosa, arai r Time (rru trab &quot; tPP

MANUAL WASHING INDICATOR LUS.:JP rodu11vi of manual washing [Distance from Lman / (Number of full-time changers χ Time of Lman} J,, "Mechanical washing Ltl .1.0 Water consumption ( Volume of water / Distance of lmec (rd. DafA) LU. Fuel consumption (Volume of diesel fuel / lmc time) Difficulty of drying the oil (Distance from Lmec / (Number of full-time workers) Lmec Time (Lmec) Time (hours) 1, h'J :) F Economic Indicators ^ QCIXC £ 0 Indicator Description dn ages Sweep Μία i Sweep chasm (distance Scanning costs / scanning distance (€, km'1) hlhs Cost of scanning (scanning time) [Scanning costs / (Scanning time) Scanning time (scanning time) (€? G)? 1) Wash 3 Washing cost (distance) (Washing expenses / Washing distance (€. Km 'L) Code Indicator Description of the AI ;, &lt; Cust e of the 1st vagam (trap time) fite to that of the .isesueur / (Ivónero tt: u; ba .1 hadottes: in time integrate the fempa de levagee) J : € v work 'd ri'1)

Β - Evaluation of .Doserguendo ^ mciautaX The proposed model will evaluate the performance of the aquila. (ECLAC), which will be used as a starting point for the environmental assessment of the region, the deposition of waste in aquifers, the final balance, the scale of entry into the waste disposal (landfill) or tine collection or sorting units); as from the start of the operations of carriages or laundering of the streets and end of the road, the entry into the waste water treatment plants and the temporary transfer (mechanical sweeping) or in the garage (other operations) , The M · D environmental performance assessment is coincident oom. the loyalty phase of the AmPlental Life Cycle Analysis (AIACv) Impacte in which the beginning of the Cycle of Inertia of the Cycle of Life (ICV) is rounded up to a limited set of environmental information on the environmental profile of the service or of the System Management Operations (Figure 1 - Conceptual Model of Environmental Performance). However, if the service is not available, 3 operations are managed by tonstitoldo by categories of impact and / or an index or environmental indicator. The impact categories allow quantification of the effects while the Environmental Index (Eco-indicator99) guarantees environmental damages resulting from the provision of the service, MA D makes the environmental performance evaluation (profile, environmental / both management system and components or operations that integrate it.> MAD performs the performance evaluation (impact / environment through the characterization of the environmental interventions or elementary finite, compiled in the Life Cycle Inventory phase.The evaluation can be limited or continuous in time the assessment of environmental performance is supported by information obtained through performance indicators and life cycle inventories or eco-vectors relating to the services, processes or operations or management components.

The characterization of the environmental impact will be used either simultaneously or indi- vidually, the methodologies of AiAC7: the CML-2001 and the Eco-iadicador99. This option allows the user to quantify the environmental profile of the service and the management operations, at the level (Eq.), environmental degradation, erosion, erosion, erosion, erosion, erosion, erosion, erosion, erosion and erosion. cover the main ones: a) Definition of the objective or the scope of the analysis; (ICV) and Environmental Impact Assessment of the AIDS Cycle (AIACPJ, AXACb requires that the MAU consult the classification of impact categories, determine Eco-Indicators, and : environmental profile, services and operations, (A) the end of the periodic report and the report,

The environmental profile of the MA D is related to the functional units '' collection of a ton of waste ', stop the service of rseoth.af and: - urban cleanliness of a linear kilometer of the street' for. to go the urban piece.

The results of the environmental assessment will translate into the larger categories of impact and of the biotechnology associated with each ton of oil. collected and to each linear kilometer of the washed and swept The recommended period of time is defined as a year, which allows for a greater number of activities that cause the impacts to be carried out, including occasional activities such as maintenance of the equipment. s delimitation of the boundaries of the system must make feasible and meet the objectives intended for each evaluation, name a.d the lover the environmental assessment of the service provided by the entities, managers. To that end, the front streets. the system must go through the integration of processes, coagronent operations of the system management, and enable its separation from the external environment, .

Although boundary constraint is conditioned by the availability of information, it should include: the main flows of energy and process energy (eg fuel and electricity) and the physical limits of the system (for example, , municipalities or parishes). The environmental performance analysis excludes the contribution of transport by users of the serotype to the collection points. &Quot; of indifferentiated and recyclable residues and considers the administrative or geographical limits of the municipalities or parishes integrated in the intervention area of the management or management system in urban waste disposal as system boundaries.

Opticians can select and adopt analytical reference points that are easy to identify by the various stakeholders in order to make it possible to compare the environmental performance of the service between different systems and managing entities. B) Life Cycle Inventory The life cycle inventory (environmental inventory) quantifies the environmental value (elemental flows or environmental interventions) generated by: the actual action of the services, according to the boundaries and functional units pre- It also allows the quantification of the environmental management of each service.

In an inventive step of the cycle, the environmental load is calculated (elementary flows) of the management operations by reference to the collection circuitry of the cocaine. This inhibition is coupled to the management and management of the system under review, and the management and operation of the system under review. The environmental balance sheet is the result of the integration and processing of the basic methodology of the three-year matrix accounting methodology: a) operational information (basic data) d: the management of the system ; (d) performance indicators (pre-selection of the proposed indicator system) and (o) eco-sectors: (elemental fl ows for resource consumption and emissions for water, water and the products or processes relating to the execution of the test in the evaluation of the operational information (base data) are used. in the characterization and construction of the environmental inventory (elementary flakes and processes of the system, by means of oxempio: deposition, removal (collection), transfer and transport of urban waste). such as the maintenance of containers and containers, etc. Operational information includes, inter alia, data relating to the circulation circuits. collection of collection ports. vehicles, equipment, type and number of containers: extension, road traffic density, esc.), water and detergent consumption, wastewater management, fuel consumption and electricity (support facilities) and container maintenance The operational use of the environmental inventory of the service during the reference period requires the collection of operational information (basic data) concerning the quantity and physical composition of the municipal waste and the various flows and ranks processed; (material composition and service life) (engine power and energy efficiency); characteristics and paths of the collection circuits and cleaning operations; the size, composition and character of the work teams, technologies, methodologies and means to each service. to the effects of the environmental assessment, it should focus on basic data to determine the most relevant environmental aspects of the service and to obtain them at the same time as the context information and the calibration variables of the operational performance indicators.

The proposed performance indicators (Table 1) used in the environmental inventory calculations are mainly indicators of the total and operational performance of the Indirect and Induced Collection (ΗIxx)

Reco 1 h.a Seiectiva de Recicláveis (RSRxth and Idsiipesa Urbana CLOkc),

The 1 ndi.cad.orss (RIxx) in the environmental censer of the Indica collection are from Irro Ά the origin of the 'feriscía are collected in. The number of inoicador.es a ti lis of the For example, if the entity collects the collection codes (eg collection of semi-submerged and semi-enclosed containers), the use of indicators in the realignment of the environmental icteutary of each type of waste collection indi.tereociao.es.

Table 3 - &quot; Indioadore® used in the unauthorized collection of the indentors

Unit veie, J íRton

Code

Indicator

Collection of collection vehicles i n d .1. f e r e n e 1. s d a:

Itlx.7 Total amount of Rhi collected * Provide residue reduction RX * .. &lt; 3XX®, s 2a

Consumption of electrical energy and supporting infra-raters Storage of containers collected by collection office Total collection distance per r. Onelaca collects loa ter, aao &quot; ':% kfáh. ton ~: ~ ocnt. hm '' km. log:;

^ X.B. 2 V H1.B.2V

Approximate collection distance t 1 ri e 1 h e d 1 Fuel consumption 1 Pet color. t o n 1, t er -r tonne collected

The gauges (ESRaxs used in the air-to-air ratio of the test paper (packages, paper and glass) are set out in the Error of the Reference Guide,

Table 4 - Table 1 - Table 2 - Table 2 - Table 2 - Indicator Code ......... ............... ..... .... ..................... .............. ... RSRA Unit. j. H ototot Gd vehicles in the r o c e 1 ha s e 1 o x e x va HSRa s Guantidade de p.Urre reida v · '. ·· *. (i.e., for example). • The consensus of the renewable energy, t or: '&quot; RSRb.It was built in support structures RSRs. Hybridization of co-operators (ooogorvtos5 in tar. Eortvi Total distance of km. Tonne of collection per ton collected Etotite distance of km.ton collection per tonne of RSRb, 14 Fuel consumption per tonne &amp; &amp;2; - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - the collection or collection line (s) of the collection of eristeorco in the litter (for example, eggs or eggs), without undifferentiated collection, if BGS operate ainajltaoeaoorro varied godeios deposition and collect etiiiea eahea eyelet indicators in ienrantário aírhrerrtai cate model and the deposition and collection. 0 inventory ariolenhai of qeetáo of acecentros and transport flows the riisiras real duos requires aor 11 race the the indicator I deserçren In the case of the noon, there is a number of indicators that will be useful in relation to the management of eenceneros and transport of flowers and rows. (for example, landfill, land sorting), the EPS operates at the same time, and varies significantly in different transport modes, such as waste streams and waste streams, as well as in the implementation of the inventory of each stream and each stream or stream being transported.

Table S-Xndic & dorssu et.ilr: sados no ió-vontàrió smóiants! # 0000 "Fros the transporto Code Xsxllcodor Unit

Consumption of foo fiei toa &quot; HIs in Ecoeentroe - Cor ': Curved of :: s ··: .ar &quot; . t or 'Ais.au and find AXaOS Dis tar:

The environmental inventory of the washing and disinfection at the collection point of surface containers and ecopont. ocomíi containers, with rseutso to specific vehicle, will use the performance indicators of the Error! The origin of the reference has not been found. These indicators support the environmental inventory of the washing / disinfection of containers by means of washing vehicles. Tàbél & S · Xrdicadorea - used in environmental inventory

The environmental inventory of the lavage / disinfection of the semi-buried containers, ecopoints and gels and vapors, by means of open tumble tanks up to three toners, equipped with pressure taps and water and sewage. Donors of Error! The origin of the reference dog was ignored, and the service was carried out: for a v i a t u ra tio ns. The environmental inventory of the clean urban area identifies the areas of malar intervention effort and makes it viable. comparison of the manual decontamination of the manual scanning, manual washing and mechanical washing of streets, squares to special zones (for example, party enclosures), the performance indicators (LOans) of the 1 nveni: r r 1 the environmental of. Urban cleaning are included in the bãfof Ά. (1), (1), (2), (2), (3) and (4) and (4), and (4) In the case of the sweepers, the sweeping machine is located in the vicinity of the manual, working at the same time. 7 Consumption of the pump will be possible in the metered sweep of the machine. mechanical scavenging, trawling, &quot; 5, h Larapem 11 &quot; U &quot;, 1 &quot;, &quot; t Fuel consumption 1, h is the value of the decal washing equipment m, tratf 1; ... · Λ i-.i. 0 M & D needs environmental inventories, life cycle or eco-inventories ~ vector.es, associated with the main processes and operations of waste management, Environmental inventories list the elementary mass and energy components, eg, consumption of resources, air emissions; soil and water) associated with a given functional unit, expressed in units of area {ex. (s), energy (sx, - ton ') and mass per unit unit (kdleorf50 kg .. m &quot; service &quot;' 1 and kg product &quot; 1.) The structure of the requested inventories must be coincident (ISO 14 000: 2006) (Table 8) • The inventory structure of the life cycle of a project (ISO 14 000: 2006)

Deity Quaatdd Notes

Category Additions

Airborne Sequestration Air For the Selection of Airborne Sequestration and Airborne Airborne Air Pollution; water © of the products and / or products of the waste management service in order to identify the road to the waste collection service and the urban environment? b reference source could not be found. ; , The environmental tent for massita service, for example. Coordination of production and maintenance of production equipment; production and mapping of. see service color; the type and quantity of fuel used; the quantum of leotard energy consumed in the collapse fractions; to the mare consumed (for example, washing of roads and containers) and their treatment (waste water). The inventories of the products are collected by the M &amp; Life cycle ® Deposition equipment Components used in the manufacture of waste disposal equipment (steel, aluminum, HDPE); Bags and tarpaulins of semi-finished containers, Mora; The functional unit should take into account the time frame of the evaluation cycle (in 1 year) and the lifetime of the containers (in years), inventories, inventories and the number of functional units expressed in units of (for example, wear and tear of tires and brakes), as well as the safety of the vehicle and its components. ;

Production, recovery or disposal of mineral oils and lubricants of motor vehicles; Consistency of vehicle smelting. Fuel consumption and combustion by the engine of the vehicles consumed. This inventory must be leased. (ie 1. torf: or I.km '' '), to the calorific value of the fuel s to the power and energy yield of the vehicles' motor. Energy supply (eg electricity and natural gas) consumed in logistical support infrastructures and operations. Itotac The environmental inventory of electrical energy (low voltage ··) must consider its matrix (percentage) of energy sources in the time horizon of the evaluation. Water and Wastewater Water consumed in the airwashing, and the use of water; treatment of waste water from the service; packaging and container cleaning detergents; of vehicles. Note: If the waste water is collected from the sewage service, the environmental inventory of your treatment should also be integrated with the model, the inventory of the hygienic detergents, and the washer fluid. e n t o f e s e v e l o u t io n s e v e t o n s e t o n t o n t o r t o n t o r t o n t o n t o n t t t t t t t (1,

The results of the life cycle inventory step will land on the inventories line of Cicie de Vada or Tah &amp; and Environmental. For example, all CCG emissions identified in the various processes and basic management operations) should be added together to obtain the value that will be included in the case study inventory table as Vin kg of. COr &quot;, The Inver table. Environmental information to list all environmental concerns. s and elemental tests: due to the satisfaction of the unit, it works by date of operation, by circuit or collection surface, by row collected, by management component and by type of waste deposition, f each new cycle. According to the scope and defined objectives, utili fi ers should verify / assess the need to address, include, or disregard environmental interventions, life cycle records, baseline data and performance performance of operations in the jurisdiction of the inventory of the service environment; (c) Assessment of the Life Cycle of the Life Cycle The high amount of numerical innovation resulting from the environmental inventory phase hinders its process, treatment, analysis and understanding. evaluation of environmental performance in the analysis of environmental inventories (on the other hand, it tries to reduce it to a limited set of numerical indicators (impact categories). • Eco-indicator9 | - The MAD closes the application s / vai sanes of the methodologies of altet, Eco-io: i caoord3 and CMiu-avBl, the option allows the individual to quantify the damages (EcG-indiaadorvSd and the environmental etho the impact of the service is the management operations associated with it. The CML-200I methodology has been linked to the high scientific rationality of its phytosanitary conditions. A. CM1-20OÍ is adopted in parellalmente a vet that the MA D uses. only the categories of impact, the description) and their characterization characterization (characterization), The steps of normalization and weighting of this methodology: na o are included in the model, tasting option does not exceed the specifics of the Ima 1410: 2006; which are useful in the creation of environmental indices. These two stages are useful in the creation of environmental indices. CA 1: -2001 enables the environmental effects (categories of impacts) of waste management to be quantified (Reference Error was not found, V in the global overview, eutrophication, classification, stratospheric ozone depletion and toxicity The categories of impacts on environmental indices are justified by the need to extend the scope of environmental performance review and not to restrict it. Although some categories of impact are still in development and involve a great deal of uncertainty, the adoption of this methodology allows for a greater range of analysis on various environmental themes of diverse geographic scope.

Table 10 - Cabà óri lymme d # impéet® C &lt; SML &quot; 2001 &quot; Used &quot; &quot; Tagoría d &quot; Impacts on H &

Factoso &lt; $ * Caaaoteri íçãçã®

AaJúifica-.t.iap .. PO.tenti & l (kg BÚ. ^ P

Global Barium Potential (%) Potassium 1european European (kg POxfXi) Potassium Ionate (kg) 4 ~ DCB9 <kg

Ozone Depletion sisa ccspaera c Ozone beple tioa E at t at t h a t h e 1 1 (kg CFC-11 and, for each category of impact, the association of the coauthor of the environmental ioterosaoao or of the water flow was as follows: in e ne ne 1a mass or in the 1o. the m-ImpMo characterization; zL W- < For the calculation of the damage, we will compare the damages caused by: (a) (b) and (b) and (b). The management of the management system and / or its management operations related to the aeration of the absolute heat in the air at the same time, The EoI indicates that it is the result of the arithmetical sum of categories of damage and indicates the environmental impact of the damage. This methodology integrates in a mandatory way the steps of MormaIIsacão and Ponderação, in order to obtain as final result an indicator or Environmental index, the Eco ·· indicator !, measured in bridges , The quantification of the final effects on the receptor is expressed through the cate of health damage Smueaaf Qaalidede donate leoseisfcemes o Recoateoa [2J, m

Category of Damage x ~ Y FDr, a? x ............. fo..xr · &quot; FNO.

Where, an is the amount of the environmental intervention or elementary flow j (energy, mass or volumes associated with the environmental load of the waste management operations;) translates the elementary damage damage earner (FHDS). standardization of the characterization of

The value of the Eco-Indicator results in the arithmetic sum of the categories of damage Human Health, Eucalyptus plantations and Resources (31,

Em - iaàtméfr W

X-X W,; r \ f &gt; &lt; . * and rs. X .......... P: ttt,; &quot; d). &quot; '·>' <Math>: m ,.

Where, it represents the value of Damage Chaaxing, FIsiDr ... &gt; The Factor d Forma Form. The Classification of Damage Characterization and the Classification Factor of Where, A, represents the Health of Humanity, B is the Age of the Fossa v. eras and resources,

The impact assessments of the impact categories may not be retrospectively adjusted according to methodologies or calculation specifications. In cases where the determined environmental integration, or flow of information in the environmental inventory? Be;. attributed to one or more categories of impact or damage, this is more than likely to be caused by the scoring of the tactical and character factors. ration .

From the characterization stage of CbCd results in a cluster of impact categories and the Eco-Boundary 19 that guaranties the potential effects of the environmental loams of processes and operations associated with defined functional capacity. The performance rating is based only on the category of impact and the R & D that are part of the environmental profile. Since the reference arable units are the fecelba and the urban cleaning reindeer, the environmental performance of the environmental profile of the functional unit defined by the characteristics of the environment, of the collection is based on the environmental profile of the collection of one tonne of undifferentiated or recyclable waste. This criterion is applied in the evaluation of the different methods of depositing and collecting waste. and. containers, are buried, and buried. The environmental profile of the collection is inviolable and selective, resulting in the integration of the environmental profiles of the various operations that comprise them (for example, the row collected and the type of deposition). main management operations (eg, water management and mechanical washing). The accidental profile of the waste management system is based on the integration of the environmental profile of the collection of waste, selective waste and urban waste.

The complexity in calculating the values of the performance evaluation calls for the development of a computer application capable of articulating and processing information on environmental performance (environmental profile) and obr. e r r e s u t io n t io n s. n t e rp r e v e s s by the various users of the service. The application of information technology can be specifically developed for this purpose. Its main objective should be to speed up the integration of the different variables that are fundamental to the CAV, from the performance and performance of the users to the users. · It must be supported by 3 types of information; (a) operational management; b) iodieadóres performance and cj life cycle inventories i eco ™ vectcree of various products and operations &gt; The. Application: Information must incorporate the conversion factor to ensure the calculation of the environmental inventory through the identification of basic data, performance indicators; and of the oil mill. The application must also have a facsimile library of the impact factors of the methodologies of the LDC-20D1 and Pd Ldd in the database (ErPOf the reference source) I should have seen the use of the environmental bar at the collecting circuit and the urban drainage circuit in order to speed up the environmental performance by building up the size of the data bases. of a fast and reliable processing recommend the chosen computer application: for presentation to the user, either in the form of a softeare dictate Excel 10031b with interface graphics on the Basic Dialog for trains and for use of the manipulation of the SQL databases (Strnctcred Qmerv. ippçnage). dplication Computer must integrate three edeeii files. two auxiliary files; ? oLoeReooi ta. x 1 s and LCI _Tutorials.ui}.] is a main file [110-Duplicates.xis] &gt;

The LCI Fsc tor and the Conver s, x1 &amp;; Excel 2003 calculation for files should be included in the basic data entry sheets, calculation files, commitment indicators, cycle times life and characterization factors.

The basic data, after collection and validation, will be inserted in the respective file: service history: tFontOsEecOlha <xisj> All the basic data, calculation variables and performance indicators required should be organized and organized into spreadsheets specific to each service. The absence of information related to any service should exclude authenticity from its registration. database, all basic data or sweeps of the calculation are relevant to the execution of the application; however, inclusion is recommended in order to give greater accuracy to the database in new evaluation cycles.

The life-cycle inventories used in each project should be: • inserted in Excel sheets with the name LOI of the asset and in turn stored in the Excel file. LCF FactorsConversion, xi] structure of life cycle inventories the reference source was not found,) which systematises the elementary flows of the processes into 4 environmental compartments (resource consumption and emissions to air, soil and water). water) 10 subcategories: of destination./origem (Error? The source of the reference was not 'bags': ...), according to the structure proposed by the database of environmental factors tCOINVEdi 1. i, li &amp; 11 &lt; &gt; &gt; &gt; &gt; Structure &quot; , Russian i .a. Rcr ·: '; (b) (a) (b) (b) (b) (b) (c) (b) (b) (b) er} becorata da agua / by exeep the magnesium. XlmwMâk titeassldawf® · pe-pula cl ot i hígh poptPi e t ien domei ty &gt; air Emission · mainspring emitted from the vicinity of the protected area and at the same time to protect the eepéoiec threatening to take epoe, useful for industry / center emitter, , i η oin er the heart rt, highway i ri. irtir; In the same manner as in the present invention, the dispersion of the particles in the atmosphere is carried out in the same manner as in the present invention. energy, and, therefore, the tertiary energy of the earth's atmosphere and the atmosphere of rare earth, among other future emissions, 100 years of population OX1U.1 (Igw plasma asphalt) after the start of the process Applied, for example, to radioactive waste, Tropo &amp;amp;amp;amp;amp; of airplanes. Applied to air transport * Specified category {nnspecified} Classification used if no &amp; there is the fondation of stonewall. Agricola {aqr.i &amp; ul t ura i) the soil is removed from the soil by the soil for the production of plants (fl owers and renewable) which are part of the chain. to add. (industrial and industrial) and industrial (industrial and industrial) and industrial (industrial) industries (industrial and non-industrial) Six months later, at the time of the stage, the iron phase (Wate Emissions ruthenium / iOd years after the beginning of the prose.) Applied, for the first time, to the (1) Lagoon (iske) Emissions to lakes of the oceanic ocean (oceou) Pt isoions to oceans, seas and lagoon of salt water, in the inventoric form of cemeteries in ciffbhtrre. This will allow you to group together the effluent flows from the inventory, and to collect the inventories from the inventories. This will allow you to group together the cash flows from the inventories. I like the sounds to co-measure environmental times in sub-categories. giving greater accuracy in the subsequent classification of the environmental effects of the study by allowing the use of the correspondence between the elementary flows, listed in the Inventory table, and the faotores de c a. (s) of the impact assessment (impact categories) of pollution damage (Eco · "indioaderad") shall be included in the file [XíÇX ..... Faot GresCooversao, xlsj of the sheet Excel 1 FaetvCara.ct, xis), on the other hand, must integrate a library of rCiDb that have the characterization {Error! The origin of the refer- ence was not concise; and their arrangement (in the categories or subcategories) should coincide with the structure of the life cycle inventories: Error5 The origin of the reference was not found, such a problem, the environmental effects of the United States flows into the environment,

Table 12 - Factors for the characterization of the impact and damage of MM &gt;

Methodology Impact category Tot al Acid.liication pcdential (kg; 30-t; p 15 Climate change GdPlOQa (kg CCr; &gt;.: D 1 € 0 CMt 2001 Eatropbieation potential: / average European (kg K0xe6 6 10 Bnman Toxicity HTF 10Da (kg 4 ~ DCB.e.fi) Other Ozone Depletion OOP 20a (kg CFC-11,; sq) 669 60 B-D-Characterization factor 108 lodlator 90 weighted 6 lethal ·; 000 , April 5, 20X3

Claims (9)

1, The Infrastructure Method for Evaluating the Quality of Service for the Collection of Arcanum and Urban Waste, which is characterized by its function as follows: the ideoti fi cation: the docu- mentation of the session, as well as its calculation formula for assessments of the quality of service: c, os i mal caberes: are sistematirados de were :. coherent and articulated group of indicators; c, the environmental assessment is conditioned to the calculation of the performance indicators, the valuation of banknote 1 is supported; methodology of analysis of the closure cycle; and advises: construction of a computer application for the evaluation of docempenhc, 2, Computer method for evaluating the quality of the service of the collection of urban and urban waste according to the. the previous claim characterized because it is necessary to calculate the rtsntrr performance indicators. 3, the computerized evaluation of the quality of service for the collection of urban waste and urban waste in accordance with the previous claim characterized by its adaptability to different types of waste, for example undifferentiated waste, recyclable waste such as paper, ombalagene and glass; s of urban imitation like sweeping and washing streets, among others. i. Method of application of the equation < &gt; of the quality of the urban and urban waste collection service according to the above claim characterized by adaptability to different types of waste collection, for example superfine containers: half-filled containers, bags, baskets, among others, 5, Computer method of evaluating the quality of service of urban wastewater and urban reign according to the role indexation 1 character by defining a temporal unit of the day, week, month and year and geographic as Municipality or Municipalities' A method of evaluating the quality of the urban waste collection and urban waste collection service according to claim 1 characterized by establishing predefined performance indicators for evaluating the environmental performance of the service, and a method for evaluating the quality of the service. urban and urban waste collection service according to claim 1 comprising two non-exclusive methodologies for assessing the environmental impact of the service: ΟΜ1 ··· 7001 and SCOθ1. 8. Methodology for the assessment of the quality of service of the collection of urban waste and urban cleaning in accordance with the criteria laid down by the assessment of the performance of the service as a result of the integrated analysis of its parf.il The method of determining the quality of the urban waste and urban waste services according to the preceding claims is characterized by defining the methodologies for the determination of the variables neoosaárlas to the calculation of the Indians. A method of computing the method of claim 1, wherein the age of the robotic air cleaner is cleaned according to the preceding claims, characterized by the historical design of the performance rating and producing the report according to : the number of di erentants in terms of age, 11, Methodological information on the quality of service of collection of urban roaidoos and the urban reign according to the king rations carried out by this upgrade could be carried out either by means of a computerized application in Ezcel developed aspecific for the affecito, 12, Computer method for assessing the quality of the waste collection service: urban waste and urban waste as agreed by the former for being applicable in several evaluation cycles not to see that it defines the methodology for collecting the necessary information the ratio of caries and performance indicators. A computer method for evaluating the quality of service of urban waste and urban waste collection service according to the previous claims, characterized by combining the performance indicators with. analysis of the environmental cycle in the evaluation of the environmental quality of the service. Royal villa, 5 of .hbrii of 1013