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Issues in Social and Environmental Accounting
Vol. 4, No. 2 December 2010
Pp 89-103


        Environmental Management Accounting
          (EMA) Case Studies in Honduras –
             an Integrated UNIDO Project
                                          Christine Jasch
                    Institute for environmental management and economics
                                       IÖW Vienna, Austria

                                            Daniel Ayres
                                      Cleaner Production Centre
                                              Honduras

                                      Ludovic Bernaudat
                                                  UNIDO
Abstract

This article describes the outline and main first results of the UNIDO TEST (Transfer of
Proven Practices for Environmentally Sound Technologies) program, which uses Environ-
mental Management Accounting (EMA) for setting the baseline for calculating savings
achieved by the Cleaner Production approach. The project focuses on the Rio Blanco basin in
North Western Honduras and applies an integrated approach for improving industrial water
management, pollution reduction and productivity.

Keywords: Integrated environmental management, industrial water management, environ-
mental management accounting, environmental costs, material flow cost accounting

Background                                                mental management accounting and in-
                                                          tegrated environmental management
Industrial pollution and poor water man-                  approaches like TEST in order to con-
agement are considered key priority                       vince industries to start-up their path
problems in Honduras. There is limited                    towards a sustainable industrial develop-
experience in implementation of cleaner                   ment. Following a scientific study from
production in Honduran industries. The                    the National Research Institute
UNIDO National Cleaner Production                         (CESSCO), the Rio Blanco basin has
Centre (NCPC) has conducted most pro-                     been identified as the best case study for
jects. Therefore, the need exists to dem-                 implementation in Honduras.
onstrate cleaner production, environ-
Christine Jasch Christine Jasch is Director of the Vienna Institute for Environmental Management and Economics,
IÖW Institute for environmental management and economics, IÖW Vienna, email: Jasch.Christine@ioew.at
90     C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103


Objective                                                  proach integrating the preventive win-
                                                           win strategy into enterprise operation.
The overall objective of this UNIDO                        TEST is building on management of
project is to promote the adoption of                      change within different levels of the
best practices for industrial water man-                   management pyramid:
agement and pollution reduction. This is
in line with UNIDO´s holistic approach                                 the operational level
to Cleaner Production (1). Two indus-                                  the management system level
trial sectors, textile and food production,                            and
have been selected as target for the dem-                              the strategic level.
onstration activities. The focus of the
project is on integrated water manage-                     Relevant tools of preventive environ-
ment, but also pollution related aspects                   mental management or their parts are
are addressed. The project’s objective is                  applied based on a complex diagnosis of
in line with national priorities.                          enterprise needs (Initial Review). TEST
                                                           is supporting the concept of the learning
The project is expected to deliver the                     organization starting with the identifica-
following results:                                         tion of potential leverage points and set-
     Raised awareness of industries on                     ting up the relevant baselines, ending
     the economical and environmental                      with a reflection at strategic level of the
     benefits of implementing TEST and                     improvements achieved and of the ex-
     EMA                                                   perience gained. TEST was already suc-
     Enhanced technical skills of indus-                   cessfully applied within the Danube
     tries’ staff to identify best practices               River Basin. Its integrated approach has
     for water management                                  been tailored for application to pilot
     Implementation of demonstration                       countries within the Mediterranean Re-
     solutions for better water manage-                    gion (Egypt, Morocco and Tunisia)
     ment                                                  within the framework of the MED-TEST
     Identification of demonstration                       initiative (2008-2011) as well as Hondu-
     EST investment projects to achieve                    ras and Mexico.
     national and international standards
     for water consumptions and efflu-                     A TEST project is tailored to the unique
     ent release                                           conditions of the industrial sector as well
     Established national capacity for                     as the institutional framework of the
     streamlining TEST and EMA in the                      country where it is implemented. Intro-
     industrial sector with the support of                 duction of the TEST integrated approach
     the NCPC.                                             at the enterprise level follows this se-
     Wide dissemination of project’s                       quence: first, the existing situation is
     results                                               improved by better management of the
                                                           existing processes, then the introduction
                                                           of new cleaner technology (or if not suf-
Project outline of the overall UNIDO                       ficient also of optimized end-of-pipe
TEST approach in Honduras                                  solutions) is considered. Finally, the les-
                                                           sons learned from each TEST project’s
The TEST approach developed by                             implementation is reflected in the re-
UNIDO is a need driven systematic ap-                      spective company’s business strategy.
C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103   91


Implementation of the integrated TEST                     grated approach in selected industrial
approach is based on three basic princi-                  sectors and disseminating project’s re-
ples:                                                     sults at the national level. The project
                                                          targets local industries (large and me-
1.   At the level of processes, it gives                  dium) within selected sub-sectors in in-
     priority to the preventive approach                  dustries located in the catchment area of
     of CP (Cleaner Production - sys-                     the Rio Blanco, one of the affluent of the
     tematic preventive actions based on                  ULUA river the Second´s River in the
     pollution prevention techniques                      country, located in the Sula Valley in the
     within the production process) and                   vicinity of San Pedro Sula, the country’s
     considers the transfer of additional                 industrial area.
     technologies for pollution control
     (end-of-pipe) only after the feasible                The implementation is organised into
     cleaner production solutions have                    three main phases. At project’s start a
     been explored. This leads to a                       consultation process was initiated with
     transfer of technologies aimed at                    key stakeholders, such as governmental
     optimizing environmental and fi-                     institutions and industrial associations,
     nancial performance at the same                      to discuss the project’s implementation
     time: bringing desired win-win so-                   strategy and make the final selection on
     lution for both areas.                               the industries to be targeted. A project
2.   At the level of management sys-                      steering committee was established.
     tems, the integrated TEST approach                   During the first phase a first training
     addresses the managerial aspects of                  session was organized to train the na-
     preventive environmental manage-                     tional counterpart on the TEST inte-
     ment. It establishes the necessary                   grated approach. Awareness raising
     information system on relevant ma-                   meetings were organized for the selected
     terial, energy and related financial                 industries. Formal agreements were
     flows necessary for linking the stra-                signed with these companies to secure
     tegic and operational level within                   their commitment and co-financing to
     an enterprise. This is done by using                 the project.
     the basic elements of an EMS
     (Environmental Management Sys-                       The project has now entered its second
     tem) and EMA (Environmental                          phase, were the environmental manage-
     Management Accounting).                              ment accounting (EMA) tool was used
3.   At the strategic level, it puts envi-                to establish a baseline of current costs in
     ronmental management within the                      order to be able to calculate savings. The
     broader strategy of environmental                    second phase started with the implemen-
     and corporate social business re-                    tation of an interactive training pro-
     sponsibilities (CSR), by leading                     gramme on the TEST and EMA ap-
     companies towards the adoption of                    proach for the targeting industries, na-
     sustainable enterprise strategies.                   tional EST (environmentally sound tech-
                                                          nologies) experts and some municipal,
These objectives will be achieved in                      industrial association and UN Techni-
Honduras by reinforcing national techni-                  cians invited to assure the future national
cal capacities, demonstrating the effec-                  dissemination of the project. The pro-
tiveness of the TEST and EMA inte-                        gramme consisted of theoretical lectures,
92     C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103


case studies from TEST projects imple-                     case studies will be prepared and pro-
mented elsewhere and concrete cases                        moted during technical workshops/
from the participating industries. The                     seminars targeting other industrial areas.
training programme was organised in                        An extensive communication campaign
three main modules: in between each                        will be implemented to target local mu-
session national sectorial experts pro-                    nicipalities, local communities and
vided guidance and technical assistance                    NGOs with the aim to raise awareness
to the enterprises’ staff helping them to                  and stimulate peer-group pressure on the
bridge the gaps between the existing and                   polluting industries at the local level.
the desired level of knowledge for the
implementation of EMA, sound water
management measures and environmen-                        Stakeholders and implementation is-
tally sound technology (EST).                              sues

The first module of the training pro-                      The main counterpart for TEST in Hon-
gramme focussed on EMA and was per-                        duras are the National Cleaner Produc-
formed in the last week of August 2010.                    tion Centre (NCPC) based in San Pedro
It is described in more detail further be-                 Sula, and the National Research and Pol-
low. At the end of the interactive train-                  lutants Analysis Laboratory, CESSCO,
ing programme, technical solutions for                     based in Tegucigalpa. The NCPC has
optimising the operation of the existing                   hands-on experience in implementation
technology with improvements of the                        of Cleaner Production studies, ISO
water management systems will be iden-                     14001 (2) implementations and good
tified and implemented. Moreover the                       links with relevant stakeholders (local
technical and financial feasibility for                    authorities, industrial associations, in-
technology up-grade to reach interna-                      dustries, NGOs). The national counter-
tional standard for the water usage and                    part is responsible for: overall coordina-
pollution control will be investigated.                    tion of project’s activities, quality assur-
For each company opportunity studies                       ance in line with the proposal, identifica-
will be prepared. In order to facilitate                   tion and engagement of qualified secto-
EST investments, the project shall create                  rial expertise for activities under phase
a link with financial institutions or na-                  II.
tional programmes that are offering soft
loans to industries that want to imple-                    CESCCO is actively involved in each
ment cleaner technology. By the end of                     phase of the project. Its experience in the
the second phase, the results achieved at                  areas has been valuable for the selection
each company will be evaluated, dis-                       of industries and its technical capacity
cussed with top management and pre-                        will be valuable to confirm the benefits
sented to the local stakeholders.                          of the promoted techniques through the
The last phase of the project aims at dis-                 analysis of the pollution level variation
semination of project’s results for further                in the Rio Blanco.
replication within the country. A na-
tional conference will be organised in                     Relevant stakeholders involved in the
order to present project’s results to the                  project’s advisory board are, in addition
industrial community and institutional                     to the two stakeholders above-
stakeholders. A guidance document with                     mentioned, the municipality, industrial
C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103   93


                    Table 1. Project activities and success indicators
Phase 1 - Outputs:                                  Success indicators:
       Secured commitment and active                       Agreement signed with 3 industries for
       participation of major stakeholders                 participating in TEST demonstration
       Local consultants trained                           activities
       Participating industries selected
Phase 2 – outputs                                   Success indicators (at demonstration compa-
       Enterprises trained on TEST tools            nies):
       Enterprises and consultants trained                 Number of implemented CP measures
       in EMA                                              Water savings and pollution reduction
       EMA assessments performed in                        Number of people trained
       participating enterprises                           Savings and improved information sys-
       Improved water systems based on                     tems achieved
       existing technology
       Identified investment options for
       technology up-grade (EST)
       National capacity to replicate
       TEST and EMA established
Phase 3 – outputs                                   Success indicators:
       Project’s results disseminated to                   Number of demonstration industries
       relevant stakeholders at local and                  willing to continue with TEST and/or
       national level                                      EMA activities
       Awareness raised at other indus-                    Number of new industries interested to
       trial areas to promote replication                  start-up TEST replication
       activities

associations, NGOs and local industries.                  cleaner production assessments nomi-
The involvement of the industrial asso-                   nated by the NCPC, a national account-
ciations within the TEST project is im-                   ant hired as national consultant for the
portant to ensure enterprises participa-                  NCPC as well as representatives from
tion and proper dissemination of project                  the stakeholder groups, e.g. the sector
results within the industrial community.                  specific industry representatives, the
                                                          local International Labor Organisation
                                                          (ILO) and the FAO, which are both also
Project outline of the EMA counter-                       involved with environmental and health
part                                                      issues in Honduras. The training was
                                                          performed by Ludovic Bernaudat,
The above mentioned second phase                          UNIDO, Daniel Ayes, technical director
started with the implementation of an                     of the NCPC in Honduras, and Christine
interactive training programme on the                     Jasch, Institute for environmental man-
TEST and EMA approach for the target-                     agement and economics in Vienna, per-
ing industries and national EST experts,                  forming the EMA training.
as well as the identified stakeholder
groups. A one day seminar was held in                     The second day, an internal train-the-
San Pedro Sula with the active participa-                 trainers workshop was held with the en-
tion of 2 representatives of each com-                    vironmental managers of the companies
pany (the environmental manager and an                    and the national consultants. The brew-
accountant), the consultants for the later                ery case study presented in chapter 8 of
94    C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103


the book on Environmental Management                      ready built in the NCPC, future projects
and Material Flow Cost Accounting by                      are thus likely.
Christine Jasch (3) (see also book review
in this journal) and the related EMA as-                  The companies have performed the as-
sessment tool in an Excel-template                        sessment of EMA for the last business
(available for download at www.ioew.at)                   year 2008. They will themselves with
were used as a starting point for the                     assistance of the local national consult-
training. The participants were asked to                  ants perform likewise in depth investiga-
come up with a structure for the mass                     tions for the identified most polluting
balance and a process flow chart for                      processes and an update on the total en-
their operation and discuss where the                     vironment related costs for 2009. In the
most significant environmental impacts                    meantime also the cleaner production
occur. This joint training significantly                  options as described for the project
facilitated the upcoming company on-                      phase 2 will be implemented. For the
site assessments.                                         year 2010 it is envisaged, that the
                                                          cleaner production options will have
In the following days one-day work-                       been implemented and so for the total
shops to assess the total environment                     year of 2010 the improvements in envi-
related costs of the previous business                    ronmental and financial terms should
year were performed at each company.                      become visible. The current assessment
As described in (4) the first EMA as-                     of 2008 thus established the baseline in
sessment can be performed in a one to                     order to be able to actually measure im-
two days workshop in any company                          provements and at the same time clearly
based on the list of accounts for the pre-                focus on the hot spots from an environ-
vious business year. It is essential that                 mental as well as a financial point of
the accountant is present and has direct                  view.
access to his files. The assessment is
performed into an assessment template
in Excel format, which automatically                      Description of the participating com-
aggregates to a one page summary,                         panies
which is converted into a percentage
distribution of the environment related                   Between 2005 and 2006, the National
costs by environmental media impacted                     Research and Pollutants Analysis Labo-
and by the cost categories described be-                  ratory, CESCCO, conducted a pollution
low.                                                      survey of the river basin and concluded
                                                          that four large industries were partly
On the last day in Honduras of Mrs.                       responsible for the pollution observed.
Jasch, the protocols of all companies                     The level of pollution represents a high
were discussed with the group of con-                     risk for downstream populations. Since
sultants and recommendations devel-                       then, one company has closed down and
oped. In addition, an ad hoc presentation                 the three remaining companies are part
to key executives of local industries had                 of this project.
been organised, which received high
interest in applying EMA also from                        1. Novave s.a.
other companies outside the Rio Blanco
project. With the national capacities al-                 Farm Villalobos, later renamed the Poul-
C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103   95


try Villalobos, was founded in 1964. In                    of the fish life cycle. The processes are
1965 Villalobos Farm absorbed a small                      identical to the ones described for the
chicken operation in Guatemala. This                       Danish fish processing industry in (5),
poultry operation called Pollo Rey, in                     and many of the experiences could be
1972 El Salvador, beginning operations                     transferred, if the economic benefit
and marketing poultry products under                       would be clearly visible.
the brand Indian Chicken. It is on the
market only recently in Honduras and                       The water source is actually Lake Yojoa,
Costa Rica, using the prestigious brand                    but first passes by river and pipeline,
Pollo Rey here. These poultry operations                   through the turbines of the ENEE
are part of the Animal Industry Division                   (Empresa Nacional Energia Electrica, in
(DPI) Corporacion Multi-Inversiones.                       other words the national electric com-
The division has own farms for growing                     pany), and later arrives at the farm. Ap-
and fattening, hatcheries and chicken                      proximately 14 cubic meters of water
processing plants, generating more than                    per second are available to the company.
14,000 jobs in the region.
                                                           The farm has the capacity to produce
The company Noraves as a daughter of                       8200 metric tons of whole tilapia or
DPI has 400 employees and is process-                      5500 pounds of tilapia fillets per year.
ing about 75.000 chickens per day. The                     Other products generated by the com-
organic wastes (feathers, blood, meat                      pany include: skins, scales, fishmeal,
and chicken bones) are processed in the                    and fish oil. The company manages and
flour plant attached to it, which has huge                 has the facilities for all processed prod-
water consumption and related wastewa-                     ucts: fillet product plant, fish meal and
ter treatment issues.                                      fish oil plant.

2. Aquacorporacion de Honduras                             The company exports both fresh fillets
                                                           and fresh gutted whole fish to the USA.
Aquacorporacion de Honduras is a fully                     Skins and scales are also exported.
integrated tilapia fish farm and process-                  Whole gutted whole fish, fish meal and
ing facility with about 360 employees.                     fish oil are sold domestically.
The company is located just outside of
the town Rio Lindo, at the base of                         Also included in the infrastructure of the
mountain range in which Lake Yojoa                         farm are basic water treatment systems
resides. The farm is approximately 120                     (sedimentation ponds and oxidation
hectares in size.                                          ponds) which pre-treat waste waters
                                                           prior to their re-entering the natural river
The production of the tilapia occurs in a                  systems. Probiotic products are also
variety of aquaculture systems ranging                     regularly added to these oxidation ponds
from moderate density mud bottom                           in order to more rapidly break down
ponds to high density concrete raceways.                   solid waste.
All facets of the tilapia life cycle are
managed within the production systems,                     3. Caracol Knits and Coral Knits
from reproduction to market. The pro-
duction facets include: reproduction,                      Caracol and Coral Knits are Textile
larval, nursery, juvenile, and adult stages                Plants Located in the municipality of
96    C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103


Potrerillos, Cortés Honduras that started                       monetary information on environ-
operation in 2001. The Companies are                            ment-related costs, earnings and
known both locally and internationally                          savings.
as a leader in the textile sector and are
one of the major employers in northern                    Simply defined, environmental manage-
Honduras.                                                 ment accounting (EMA) is management
                                                          accounting (MA) with a focus on physi-
The facilities include warehouses for                     cal information on the flow of energy,
storing raw materials, finished products,                 water, products and materials as well as
and spare parts, as well as a steam gen-                  monetary information on environ-
eration system with boilers operated on                   mental costs and revenues and projects
bunker and diesel fuel. The project also                  related to environmental protection.
calls for an untreated sewage water treat-                EMA is closely related to process cost-
ment plant and a plant for treating do-                   ing as well as to environmental perform-
mestic sewage and industrial wastewater                   ance and management systems. Well-
from the dyeing process.                                  designed and implemented EMA helps
                                                          to ensure better internal management
The Companies are a model in the Hon-                     and decision-making e.g. for investment
duran textile industry that are adding                    appraisal, cleaner production, improving
value to traditional maquila operations                   Eco-efficiency and calculating savings
by making greater industry integration                    within organizations. EMA also serves
and consolidation possible.                               as a basis for external reporting and life
                                                          cycle assessments of products (1).
Caracol and Coral actively take care of
their environmental responsibility,                       Starting point for EMA is the assessment
knowing that one of the biggest environ-                  of a material flow balance, also called
mental aspects related to textile produc-                 mass balance or input output balance in
tion is waste water treatment that comes                  volumes and monetary terms on the sys-
from the dyeing process. The sites have                   tem boundary of the organization for the
two Waste Water Treatment Plants, both                    complete previous business year, as
based on activated sludge and proudly                     most data is available only for this sys-
carries an ISO 14.001 certificate.                        tem boundary (7). This is especially the
                                                          case for small and medium sized compa-
                                                          nies (SMEs), which often don’t have
EMA Methodology                                           well developed cost accounting struc-
                                                          tures. In the first step of developing the
According to the definition developed                     material flow balance sheet, only a
by the United Nations EMA Expert                          rough overview analysis may be per-
Working Group (6), Environmental                          formed, instead of a detailed data collec-
Management Accounting, EMA is the                         tion.
identification, collection, analysis and
use of two types of information for inter-                The upcoming ISO standard on Material
nal decision making:                                      Flow Cost Accounting, ISO 14051:CD,
     physical information on the use,                     2009 (8), defines MFCA as “a system
     flows and destinies of energy, water                 for measuring the flow and stock of ma-
     and materials (including wastes) and                 terials in processes or production lines in
C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103   97


both physical and monetary units”.                               All purchased materials must by
MFCA is a tool for improving material                            physical necessity leave the com-
productivity in order to reduce the rela-                        pany either as product or waste and
tive consumption of materials, energy                            emission.
and water and closely linked to EMA.                             Waste is a material which has been
MFCA is regarded as an effective means                           purchased and paid for but which
by which organizations can simultane-                            has not turned into a marketable
ously seek environmental and economic                            product.
benefits. MFCA improves material pro-                            Waste is being paid for 3 times: at
ductivity in processes or production                             purchase, at production and for dis-
lines and may consequently help reduc-                           posal
ing related environmental impact. In                             Waste comprises all non-product
MFCA, the flow and amount of the in-                             output of input materials includ-
ventory of materials used within an or-                          ing water and energy.
ganization are measured in physical
units (e.g. weight, capacity, and volume)                  The EMA Assessment Template (in
and subsequently evaluated in monetary                     Microsoft Excel format, available for
units, which are based on the manufac-                     download at www.ioew.at) assists at the
turing costs incurred.                                     assessment of total annual environ-
                                                           mental and material flows and related
EMA places a particular emphasis on                        costs and provides the option to distrib-
materials and related costs because (9):                   ute them to different cost centers, which
                                                           should be equivalent to production proc-
1.   the use of energy, water and materi-                  esses and therefore provide good quality
     als, as well as the generation of                     data for investment appraisal of specific
     waste and emissions, are directly                     processes. For material flow cost ac-
     related to the environmental impacts                  counting (MFCA) the system boundary
     of organizations and their products                   for the material flows can focus on more
     (10), and                                             detailed processes within a cost centre.
2.   material purchase costs and materi-
     als lost in waste and emissions are                   The EMA Excel-template consists of
     the most prominent cost drivers in                    four sheets – Mass balance, Detail, Sum
     many organizations. Especially in                     and Structure. Information is only added
     countries with low enforcement of                     into the Mass balance and the Detail
     legal compliance and relatively low                   sheet.
     labor costs, material and energy use
     and related losses are a significant                  The Mass balance records the physical
     cost driver (12).                                     and monetary values of material inputs
                                                           and product outputs in one work step, as
Both, the EMA and MFCA approach                            these amounts should be consistent. The
have the underlying assumption, that all                   excel template contains two columns for
purchased materials must by physical                       the source of information for both val-
necessity leave the company either as                      ues. The enterprise resource planning
product or waste and emission. Waste is                    system and the accounts for materials
thus a sign of inefficient production:                     used for production should provide this
                                                           information in a consistent and detailed
98     C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103


manner.                                                    ferred to the sheet Sum to have an over-
                                                           view and a better presentation layout
The actual cost assessment is performed                    which shows the aggregated totals by
in the Detail sheet only. It can be done in                cost category and calculates the costs
any currency, which should be noted in                     into percentages to show the most rele-
the heading where EURO stands in the                       vant environment related costs. This fig-
tool.                                                      ure can also be compared to total pro-
                                                           duction costs.
All the cost categories are already set
but the several different cost items re-                   The main EMA cost categories de-
lated to cost accounts or taken from cost                  scribed in the IFAC EMA guidance
centre reports should be listed with indi-                 document (10) are shown in Figure 1.
cating the reference.
The program automatically aggregates                       For company internal calculation of en-
the costs of each cost category, but when                  vironmental costs, expenditures for envi-
adding lines to fill in more details a last                ronmental protection are only one part of
cross check is recommended to make                         the coin. The costs of waste and emis-
sure all aggregates are complete.                          sions include much more then the re-
The sum of the costs of all categories in                  spective treatment facilities and disposal
the sheet Detail is automatically trans-                   fees. Several EMA and MFCA case

     Material Flow related Costs

     1. Materials Costs of Product Outputs

     2. Materials Costs of Non-Product Outputs

     Environmental Protection related Cost

     3. Waste and Emission Control Costs

     4. Prevention and other Environmental Management Costs


                         Figure 1: MFCA and EMA cost categories

studies have shown that the costs of                       ronmental costs in relation to other
waste disposal and emission treatment                      costs. However, it is not the goal to
are typically 1 – 20 % of total environ-                   show that environmental protection is
mental costs, while the purchase costs of                  expensive, but rather to highlight the
the wasted materials represent 40 to 90                    scope for savings potentials. It is also
% of environmental costs, depending on                     not the most important task to spend a
the business sector examined (13), (14),                   lot of time defining exactly which costs
(15) .                                                     are environmental or not, or what per-
                                                           centage of something is environmental
Adding the purchase value of non-                          or not, or if Energy belongs to NPO and
product output to the corporate environ-                   to what degree. Environmental protec-
mental costs increases the share of envi-                  tion projects not only have effects on
C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103   99

       Environmental protection expenditure (emissions treatment, control and waste pre-
       vention costs)
+      Costs of Non Product Output (Costs of unproductive material, capital, and personnel)
=      Total corporate environment related costs

                  Figure 2: Total corporate environment related costs


nature, but also on neighbors (noise,                      In other words, corporate environmental
odors, pollution) and employees (health                    and material flow costs are just a subset
and safety), if related to material and                    of the bigger cost universe that is neces-
energy flows. In addition they result in a                 sary for good decision-making. Environ-
reduction of risks for employees, nature                   mental costs are part of an integrated
and neighbors in case of accidents and                     system of materials, energy and money
other occasional production events.                        flows through a corporation, and not a
                                                           separate type of cost. Doing EMA and
It is often difficult to determine the envi-               MFCA is simply doing better, more
ronmental portion of these costs. As                       comprehensive Management Account-
with integrated cleaner technologies that                  ing, while wearing an environmental hat
are often more cost and material effi-                     that opens the eyes to hidden costs.
cient, the environmental portion of                        Therefore, the focus of MFCA is no
health and safety or risk prevention ac-                   longer on assessing total environmental
tivities usually cannot be determined                      costs, but on a revised calculation of
precisely. In general, it may be stated                    production costs on the basis of material
that assets that are allotted 100% to the                  flows (including energy and water).
environment are bad for the environment
as they are often end-of-pipe technolo-
gies that do not solve the problem at the                  Results of the EMA assessments
source, but rather shift it from one envi-
ronmental medium to another (e.g. from                     Starting point of an EMA project is put-
the air to the soil and then into the wa-                  ting the right team members together.
ter). These approaches are expensive                       Experience shows that the environ-
and inefficient.                                           mental manager barely has access to the
                                                           actual cost accounting documents of the
The most important task is to make sure                    company and only is aware of a tiny
that ALL relevant and significant costs                    fraction of aggregate environmental
are considered when making business                        costs. On the other hand, the financial
decisions. This is why Figure 2 calls the                  accountant/controller does have most of
total sum: total environment related                       the information but is unable to separate
costs. This is the universe of costs, that                 the environmental part without further
the environmental manager deals with                       guidance. In addition, he or she is lim-
and that can possibly be reduced by pol-                   ited to thinking within the framework of
lution prevention and material and en-                     existing accounts. Also, the two depart-
ergy efficiency projects.                                  ments tend to have a severe language
                                                           problem.
100     C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103


So combining the competencies for                          Using the explanations of the EMA
monetary accounting and process engi-                      books and the Excel Template provided
neering/environmental management and                       with it, the first EMA assessment for the
gaining support from both sides is vital                   previous business year for any given
for the success of any EMA project.                        company should not take longer than a 1
                                                           to 2 days workshop with the accountant
Another important guideline on the way                     and process engineer.
is to focus the assessments on what is
easily available from existing records                     The cost assessment reveals improve-
and to note, where improvements to the                     ment options in two areas:
information system would be recom-
                                                           1.    What always can be found, are op-
mended, so that future assessments will
                                                                 tions and measures necessary to
provide better data in shorter time. It is
                                                                 improve the quality and consistency
NOT the goal of an EMA assessment to
                                                                 of data and information flows in an
come up with “complete data” for the
                                                                 organisation. This is the starting
past and spend a lot of time tracing old
                                                                 point of EMA most projects and the
invoices. It is rather the goal to open the
                                                                 focus of most follow up projects.
eye for improvement necessities and
develop an overview on the most signifi-                   2.    In companies, that have not done
cant material flows and related costs.                           environmental management pro-
                                                                 jects for several years, also techni-
The resulting recommendation for the                             cal improvement options may im-
assessment is: don’t be shy to use esti-                         mediately become obvious. What
mates! The people at the production                              always is made visible, mostly for
processes often can provide very good                            the first time, are the costs related
estimates for loss percentages, which are                        to inefficient production, wasting
much more accurate than the figures                              materials and energy. So even if the
used in the cost accounting department.                          technical solution might not be
Estimates can at a later stage be im-                            known at the end of the first assess-
proved by more detailed measurements,                            ment, the priority areas for deeper
but for the first assessment don’t worry                         investigation will have been de-
not to be perfect. It is better to have an                       fined and the total range of environ-
estimate than no figure. But the calcula-                        ment related costs will be clearer.
tion procedure or the information source
for the estimate should be recorded.                       The following table shows an aggre-
                                                           gated result of the 2 companies in Hon-
The goal of the first assessment is to                     duras from the food industry. As both
    be able to present the entire material                 companies have not installed an environ-
    inputs and total environmental costs                   mental management system yet, their
    of the previous business year to top                   costs relating to environmental protec-
    management, and                                        tion are negligible (2 % for end of pipe
    come up with improvement recom-                        treatment, most related with the waste
    mendations and                                         water treatment plant and 0,2 % for in-
    gain support to improve the infor-                     ternal personal dealing with pollution
    mation system and technical proc-                      prevention). In all the EMA case studies,
    esses.                                                 the actual costs are subject to secrecy.
C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103      101


  Figure 3: Average cost distribution in the food industry in the Honduras case
                                     studies

Environment related costs by environ-           Air and     Water and    Solid Waste       General      Total in %
mental domains and cost categories              climate        Waste                       environ-
                                                               Water                        mental
                                                                                           Manage-
                                                                                              ment
1. MATERIALS COSTS OF NON-                       20,0%           2,4%          75,3%          0,0%          97,7%
PRODUCT OUTPUTS

1.1. Raw and Auxiliary Materials                   0,0%           0,0%         70,0%           0,0%          70,0%
1.2. Packaging Materials                           0,0%           0,0%           0,1%          0,0%           0,1%
1.4. Operating Materials                           0,0%           2,4%           4,7%          0,0%           7,1%
1.5. Water                                         0,0%           0,0%           0,0%          0,0%           0,0%
1.6. Energy                                       20,0%           0,0%           0,0%          0,0%          20,0%
1.7. Processing Costs                              0,0%           0,0%           0,5%          0,0%           0,5%
2. END-OF-PIPE                                     0,0%          1,6%           0,2%           0,2%          2,0%

2.1. Equipment Depreciation                        0,0%           0,4%           0,0%          0,2%           0,6%

2.2. Operating Materials                           0,0%           0,4%           0,0%          0,0%           0,4%
2.3. Water and Energy                              0,0%           0,0%           0,0%          0,0%           0,0%
2.4. Internal Personnel                            0,0%           0,4%           0,1%          0,0%           0,5%
2.5. External Services                             0,0%           0,3%           0,0%          0,0%           0,3%
2.6. Fees, Taxes and Permits                       0,0%           0,1%           0,1%          0,0%           0,2%
2.7. Insurance                                     0,0%           0,0%           0,0%          0,0%           0,0%
2.8. Remediation and Compensation                  0,0%           0,0%           0,0%          0,0%           0,0%
3. INTEGRATED PREVENTION                           0,0%          0,0%           0,1%           0,1%          0,2%
3.1. Equipment Depreciation                        0,0%           0,0%           0,0%          0,0%           0,0%

3.2. Operating Materials, Water, Energy            0,0%           0,0%           0,0%          0,0%           0,0%
3.3. Internal Personnel                            0,0%           0,0%           0,1%          0,1%           0,2%
3.4. External Services                             0,0%           0,0%           0,0%          0,0%           0,0%
3.5. Other                                         0,0%           0,0%           0,0%          0,0%           0,0%
4. RESEARCH and DEVELOPMENT                        0,0%          0,0%           0,0%           0,0%          0,0%
COSTS
5. FINES                                           0,0%          0,2%           0,0%           0,0%          0,2%
TOTAL ENVIRONMENT-RELATED
COSTS (1. + 2. + 3. + 4. + 5. + 6.)
                                                 20,0%           4,2%          75,6%           0,3%         100,1%
7. ENVIRONMENT-RELATED
EARNINGS

7.1. Other Earnings                                0,0%           0,0%          -0,1%          0,0%          -0,1%
7.2. Subsidies                                     0,0%           0,0%           0,0%          0,0%           0,0%
TOTAL ENVIRONMENT-RELATED
EARNINGS                                           0,0%          0,0%          -0,1%           0,0%          -0,1%
TOTAL ENVIRONMENT-RELATED
COSTS & EARNINGS
                                                 20,0%           4,2%          75,5%           0,3%         100,0%
102    C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103


Therefore the table shows the average                     Jasch C., (2009) “Environmental and
percentage distribution, which allows                           Material Flow Cost Accounting -
interpretation of the most significant                          Principles and Procedures”, Eco-
cost carriers.                                                  Efficiency in Industry and Sci-
                                                                ence, Vol. 25, Vienna: Institut für
As energy is not regarded as a product in                       Ökologische Wirtschaftsfor-
the food industry, the 20 % costs for en-                       schung.
ergy can be taken as a reference point.                   Jasch Ch., (2006) “How to perform an
The by far most significant costs are re-                       environmental cost assessment in
lated to the loss of raw and auxiliary                          one day”, Journal of Cleaner Pro-
materials, which are not processed into a                       duction, Vol. 14, No 14.
marketable product. They account for 70                   Thrane M., Nielsen E., Christensen P.,
% of the total environment related costs.                       (2009) “Cleaner Production in
Even though part of the skin, blood, etc.                       Danish fsih processing – experi-
are being processes into animals feed,                          ences, status and possible future
the related income of 0,1 % is negligible                       strategies”, Journal of cleaner Pro-
in relation to the material input costs                         duction, Vol. 17, No 3, pp. 380 –
lost. Any improvement of the raw mate-                          390.
rial processing efficiency would thus                     United Nations Division for sustainable
significantly reduce costs and environ-                         Development, “Department of
mental impact, as most of the organic                           Economic and Social Affairs”,
waste ends up in the wastewater stream.                         Environmental Management Ac-
However, both companies neither moni-                           counting, Procedures and Princi-
tor the actual volumes of organic waste                         ples, (United Nations publication,
being processed in the animal feed plant                        Sales No. 01.II.A.3), www.un.org/
nor the waste volumes discharged into                           e s a/ s us t d e v/ e s t e ma 1. ht m ,
the river.                                                      www.ioew.at
                                                          Jasch Ch., (2003) “The use of environ-
By installing an environmental manage-                          mental management accounting
ment system the costs for internal and                          (EMA) for identifying environ-
external people working on integrated                           mental costs”, Journal of Cleaner
prevention will go up. At the same time                         Production, Vol. 11, September.
they would be working on reducing the                     ISO (2009) “ISO:CD 14051, Material
material costs of non-product outputs.                          Flow Cost Accounting, Geneva:
Case studies in Austria from the brewery                        International Organization for
industry have seen a reduction in the                           Standardization.
relative costs of non-product outputs to                  Jasch Ch., (2006) “Environmental man-
as low as 55 %.                                                 agement accounting (EMA) as the
References                                                      next step in the evolution of man-
                                                                agement accounting”, Journal of
UNIDO (2010) http://www.unido.org/                              Cleaner Production, Vol. 14, No.
     index.php?id=o5151, 13.3.2010                              14.
ISO (2001) ISO 14001, Environmental                       Schaltegger S, Burritt R. (2000) Con-
     Management System Specifica-                               temporary Environmental Ac-
     tion, Geneva: International Or-                            counting – Issues, Concepts and
     ganization for Standardization.
C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103   103


       Practice. UK: Greenleaf Publish-                         menting Environmental Manage-
       ing.                                                     ment Accounting: Status and
Burritt R, Hahn T, Schaltegger S. (2002)                        Challenges, Dordrecht, NL: Klu-
       “Towards a Comprehensive                                 wer Academic Publ.
       Framework for Environmental                        K. Fichter, T. Loew and E. Seidel,
       Management Accounting – Links                            (1997)        Betriebliche
       Between Business Actors and                              Umweltkostenrechung (available
       EMA Tools”, Australian Account-                          only in German). Berlin: Springer
       ing Review, Vol. 12, No. 2, pp. 39                       Verlag.
       -50.                                               K. Fichter, T. Loew, C. Redmann and
IFAC (2005) Environmental Manage-                               M.      Strobel,        (1999)
       ment Accounting, International                           Flusskostenmanagement,
       Guidance document, New York:                             Kostensenkung und Öko-
       International Federation of Ac-                          Effizienz        durch     eine
       countants.                                               Materialflußorientierung in der
Jasch Ch., Danse M., (2005)                                     Kostenrechnung (available only in
       “Environmental Management Ac-                            German). Wiesbaden, Germany:
       counting pilot projects in Costa                         Hessisches Ministerium für
       Rica”, in Bennet M., Rikhardson                          Wirtschaft, Verkehr, und
       P., Schaltegger S. (Eds.) Imple-                         Landesentwicklung.
International Journals Call for Paper
The IISTE, a U.S. publisher, is currently hosting the academic journals listed below. The peer review process of the following journals
usually takes LESS THAN 14 business days and IISTE usually publishes a qualified article within 30 days. Authors should
send their full paper to the following email address. More information can be found in the IISTE website : www.iiste.org

Business, Economics, Finance and Management               PAPER SUBMISSION EMAIL
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Developing Country Studies                                DCS@iiste.org
Industrial Engineering Letters                            IEL@iiste.org


Physical Sciences, Mathematics and Chemistry              PAPER SUBMISSION EMAIL
Journal of Natural Sciences Research                      JNSR@iiste.org
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Engineering, Technology and Systems                       PAPER SUBMISSION EMAIL
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Control Theory and Informatics                            CTI@iiste.org
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Industrial Engineering Letters                            IEL@iiste.org
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Environment, Civil, Materials Sciences                    PAPER SUBMISSION EMAIL
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Life Science, Food and Medical Sciences                   PAPER SUBMISSION EMAIL
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11.isea vol 0004www.iiste.org call for paper no 2 pp. 89-103

  • 1. Issues in Social and Environmental Accounting Vol. 4, No. 2 December 2010 Pp 89-103 Environmental Management Accounting (EMA) Case Studies in Honduras – an Integrated UNIDO Project Christine Jasch Institute for environmental management and economics IÖW Vienna, Austria Daniel Ayres Cleaner Production Centre Honduras Ludovic Bernaudat UNIDO Abstract This article describes the outline and main first results of the UNIDO TEST (Transfer of Proven Practices for Environmentally Sound Technologies) program, which uses Environ- mental Management Accounting (EMA) for setting the baseline for calculating savings achieved by the Cleaner Production approach. The project focuses on the Rio Blanco basin in North Western Honduras and applies an integrated approach for improving industrial water management, pollution reduction and productivity. Keywords: Integrated environmental management, industrial water management, environ- mental management accounting, environmental costs, material flow cost accounting Background mental management accounting and in- tegrated environmental management Industrial pollution and poor water man- approaches like TEST in order to con- agement are considered key priority vince industries to start-up their path problems in Honduras. There is limited towards a sustainable industrial develop- experience in implementation of cleaner ment. Following a scientific study from production in Honduran industries. The the National Research Institute UNIDO National Cleaner Production (CESSCO), the Rio Blanco basin has Centre (NCPC) has conducted most pro- been identified as the best case study for jects. Therefore, the need exists to dem- implementation in Honduras. onstrate cleaner production, environ- Christine Jasch Christine Jasch is Director of the Vienna Institute for Environmental Management and Economics, IÖW Institute for environmental management and economics, IÖW Vienna, email: Jasch.Christine@ioew.at
  • 2. 90 C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 Objective proach integrating the preventive win- win strategy into enterprise operation. The overall objective of this UNIDO TEST is building on management of project is to promote the adoption of change within different levels of the best practices for industrial water man- management pyramid: agement and pollution reduction. This is in line with UNIDO´s holistic approach the operational level to Cleaner Production (1). Two indus- the management system level trial sectors, textile and food production, and have been selected as target for the dem- the strategic level. onstration activities. The focus of the project is on integrated water manage- Relevant tools of preventive environ- ment, but also pollution related aspects mental management or their parts are are addressed. The project’s objective is applied based on a complex diagnosis of in line with national priorities. enterprise needs (Initial Review). TEST is supporting the concept of the learning The project is expected to deliver the organization starting with the identifica- following results: tion of potential leverage points and set- Raised awareness of industries on ting up the relevant baselines, ending the economical and environmental with a reflection at strategic level of the benefits of implementing TEST and improvements achieved and of the ex- EMA perience gained. TEST was already suc- Enhanced technical skills of indus- cessfully applied within the Danube tries’ staff to identify best practices River Basin. Its integrated approach has for water management been tailored for application to pilot Implementation of demonstration countries within the Mediterranean Re- solutions for better water manage- gion (Egypt, Morocco and Tunisia) ment within the framework of the MED-TEST Identification of demonstration initiative (2008-2011) as well as Hondu- EST investment projects to achieve ras and Mexico. national and international standards for water consumptions and efflu- A TEST project is tailored to the unique ent release conditions of the industrial sector as well Established national capacity for as the institutional framework of the streamlining TEST and EMA in the country where it is implemented. Intro- industrial sector with the support of duction of the TEST integrated approach the NCPC. at the enterprise level follows this se- Wide dissemination of project’s quence: first, the existing situation is results improved by better management of the existing processes, then the introduction of new cleaner technology (or if not suf- Project outline of the overall UNIDO ficient also of optimized end-of-pipe TEST approach in Honduras solutions) is considered. Finally, the les- sons learned from each TEST project’s The TEST approach developed by implementation is reflected in the re- UNIDO is a need driven systematic ap- spective company’s business strategy.
  • 3. C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 91 Implementation of the integrated TEST grated approach in selected industrial approach is based on three basic princi- sectors and disseminating project’s re- ples: sults at the national level. The project targets local industries (large and me- 1. At the level of processes, it gives dium) within selected sub-sectors in in- priority to the preventive approach dustries located in the catchment area of of CP (Cleaner Production - sys- the Rio Blanco, one of the affluent of the tematic preventive actions based on ULUA river the Second´s River in the pollution prevention techniques country, located in the Sula Valley in the within the production process) and vicinity of San Pedro Sula, the country’s considers the transfer of additional industrial area. technologies for pollution control (end-of-pipe) only after the feasible The implementation is organised into cleaner production solutions have three main phases. At project’s start a been explored. This leads to a consultation process was initiated with transfer of technologies aimed at key stakeholders, such as governmental optimizing environmental and fi- institutions and industrial associations, nancial performance at the same to discuss the project’s implementation time: bringing desired win-win so- strategy and make the final selection on lution for both areas. the industries to be targeted. A project 2. At the level of management sys- steering committee was established. tems, the integrated TEST approach During the first phase a first training addresses the managerial aspects of session was organized to train the na- preventive environmental manage- tional counterpart on the TEST inte- ment. It establishes the necessary grated approach. Awareness raising information system on relevant ma- meetings were organized for the selected terial, energy and related financial industries. Formal agreements were flows necessary for linking the stra- signed with these companies to secure tegic and operational level within their commitment and co-financing to an enterprise. This is done by using the project. the basic elements of an EMS (Environmental Management Sys- The project has now entered its second tem) and EMA (Environmental phase, were the environmental manage- Management Accounting). ment accounting (EMA) tool was used 3. At the strategic level, it puts envi- to establish a baseline of current costs in ronmental management within the order to be able to calculate savings. The broader strategy of environmental second phase started with the implemen- and corporate social business re- tation of an interactive training pro- sponsibilities (CSR), by leading gramme on the TEST and EMA ap- companies towards the adoption of proach for the targeting industries, na- sustainable enterprise strategies. tional EST (environmentally sound tech- nologies) experts and some municipal, These objectives will be achieved in industrial association and UN Techni- Honduras by reinforcing national techni- cians invited to assure the future national cal capacities, demonstrating the effec- dissemination of the project. The pro- tiveness of the TEST and EMA inte- gramme consisted of theoretical lectures,
  • 4. 92 C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 case studies from TEST projects imple- case studies will be prepared and pro- mented elsewhere and concrete cases moted during technical workshops/ from the participating industries. The seminars targeting other industrial areas. training programme was organised in An extensive communication campaign three main modules: in between each will be implemented to target local mu- session national sectorial experts pro- nicipalities, local communities and vided guidance and technical assistance NGOs with the aim to raise awareness to the enterprises’ staff helping them to and stimulate peer-group pressure on the bridge the gaps between the existing and polluting industries at the local level. the desired level of knowledge for the implementation of EMA, sound water management measures and environmen- Stakeholders and implementation is- tally sound technology (EST). sues The first module of the training pro- The main counterpart for TEST in Hon- gramme focussed on EMA and was per- duras are the National Cleaner Produc- formed in the last week of August 2010. tion Centre (NCPC) based in San Pedro It is described in more detail further be- Sula, and the National Research and Pol- low. At the end of the interactive train- lutants Analysis Laboratory, CESSCO, ing programme, technical solutions for based in Tegucigalpa. The NCPC has optimising the operation of the existing hands-on experience in implementation technology with improvements of the of Cleaner Production studies, ISO water management systems will be iden- 14001 (2) implementations and good tified and implemented. Moreover the links with relevant stakeholders (local technical and financial feasibility for authorities, industrial associations, in- technology up-grade to reach interna- dustries, NGOs). The national counter- tional standard for the water usage and part is responsible for: overall coordina- pollution control will be investigated. tion of project’s activities, quality assur- For each company opportunity studies ance in line with the proposal, identifica- will be prepared. In order to facilitate tion and engagement of qualified secto- EST investments, the project shall create rial expertise for activities under phase a link with financial institutions or na- II. tional programmes that are offering soft loans to industries that want to imple- CESCCO is actively involved in each ment cleaner technology. By the end of phase of the project. Its experience in the the second phase, the results achieved at areas has been valuable for the selection each company will be evaluated, dis- of industries and its technical capacity cussed with top management and pre- will be valuable to confirm the benefits sented to the local stakeholders. of the promoted techniques through the The last phase of the project aims at dis- analysis of the pollution level variation semination of project’s results for further in the Rio Blanco. replication within the country. A na- tional conference will be organised in Relevant stakeholders involved in the order to present project’s results to the project’s advisory board are, in addition industrial community and institutional to the two stakeholders above- stakeholders. A guidance document with mentioned, the municipality, industrial
  • 5. C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 93 Table 1. Project activities and success indicators Phase 1 - Outputs: Success indicators: Secured commitment and active Agreement signed with 3 industries for participation of major stakeholders participating in TEST demonstration Local consultants trained activities Participating industries selected Phase 2 – outputs Success indicators (at demonstration compa- Enterprises trained on TEST tools nies): Enterprises and consultants trained Number of implemented CP measures in EMA Water savings and pollution reduction EMA assessments performed in Number of people trained participating enterprises Savings and improved information sys- Improved water systems based on tems achieved existing technology Identified investment options for technology up-grade (EST) National capacity to replicate TEST and EMA established Phase 3 – outputs Success indicators: Project’s results disseminated to Number of demonstration industries relevant stakeholders at local and willing to continue with TEST and/or national level EMA activities Awareness raised at other indus- Number of new industries interested to trial areas to promote replication start-up TEST replication activities associations, NGOs and local industries. cleaner production assessments nomi- The involvement of the industrial asso- nated by the NCPC, a national account- ciations within the TEST project is im- ant hired as national consultant for the portant to ensure enterprises participa- NCPC as well as representatives from tion and proper dissemination of project the stakeholder groups, e.g. the sector results within the industrial community. specific industry representatives, the local International Labor Organisation (ILO) and the FAO, which are both also Project outline of the EMA counter- involved with environmental and health part issues in Honduras. The training was performed by Ludovic Bernaudat, The above mentioned second phase UNIDO, Daniel Ayes, technical director started with the implementation of an of the NCPC in Honduras, and Christine interactive training programme on the Jasch, Institute for environmental man- TEST and EMA approach for the target- agement and economics in Vienna, per- ing industries and national EST experts, forming the EMA training. as well as the identified stakeholder groups. A one day seminar was held in The second day, an internal train-the- San Pedro Sula with the active participa- trainers workshop was held with the en- tion of 2 representatives of each com- vironmental managers of the companies pany (the environmental manager and an and the national consultants. The brew- accountant), the consultants for the later ery case study presented in chapter 8 of
  • 6. 94 C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 the book on Environmental Management ready built in the NCPC, future projects and Material Flow Cost Accounting by are thus likely. Christine Jasch (3) (see also book review in this journal) and the related EMA as- The companies have performed the as- sessment tool in an Excel-template sessment of EMA for the last business (available for download at www.ioew.at) year 2008. They will themselves with were used as a starting point for the assistance of the local national consult- training. The participants were asked to ants perform likewise in depth investiga- come up with a structure for the mass tions for the identified most polluting balance and a process flow chart for processes and an update on the total en- their operation and discuss where the vironment related costs for 2009. In the most significant environmental impacts meantime also the cleaner production occur. This joint training significantly options as described for the project facilitated the upcoming company on- phase 2 will be implemented. For the site assessments. year 2010 it is envisaged, that the cleaner production options will have In the following days one-day work- been implemented and so for the total shops to assess the total environment year of 2010 the improvements in envi- related costs of the previous business ronmental and financial terms should year were performed at each company. become visible. The current assessment As described in (4) the first EMA as- of 2008 thus established the baseline in sessment can be performed in a one to order to be able to actually measure im- two days workshop in any company provements and at the same time clearly based on the list of accounts for the pre- focus on the hot spots from an environ- vious business year. It is essential that mental as well as a financial point of the accountant is present and has direct view. access to his files. The assessment is performed into an assessment template in Excel format, which automatically Description of the participating com- aggregates to a one page summary, panies which is converted into a percentage distribution of the environment related Between 2005 and 2006, the National costs by environmental media impacted Research and Pollutants Analysis Labo- and by the cost categories described be- ratory, CESCCO, conducted a pollution low. survey of the river basin and concluded that four large industries were partly On the last day in Honduras of Mrs. responsible for the pollution observed. Jasch, the protocols of all companies The level of pollution represents a high were discussed with the group of con- risk for downstream populations. Since sultants and recommendations devel- then, one company has closed down and oped. In addition, an ad hoc presentation the three remaining companies are part to key executives of local industries had of this project. been organised, which received high interest in applying EMA also from 1. Novave s.a. other companies outside the Rio Blanco project. With the national capacities al- Farm Villalobos, later renamed the Poul-
  • 7. C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 95 try Villalobos, was founded in 1964. In of the fish life cycle. The processes are 1965 Villalobos Farm absorbed a small identical to the ones described for the chicken operation in Guatemala. This Danish fish processing industry in (5), poultry operation called Pollo Rey, in and many of the experiences could be 1972 El Salvador, beginning operations transferred, if the economic benefit and marketing poultry products under would be clearly visible. the brand Indian Chicken. It is on the market only recently in Honduras and The water source is actually Lake Yojoa, Costa Rica, using the prestigious brand but first passes by river and pipeline, Pollo Rey here. These poultry operations through the turbines of the ENEE are part of the Animal Industry Division (Empresa Nacional Energia Electrica, in (DPI) Corporacion Multi-Inversiones. other words the national electric com- The division has own farms for growing pany), and later arrives at the farm. Ap- and fattening, hatcheries and chicken proximately 14 cubic meters of water processing plants, generating more than per second are available to the company. 14,000 jobs in the region. The farm has the capacity to produce The company Noraves as a daughter of 8200 metric tons of whole tilapia or DPI has 400 employees and is process- 5500 pounds of tilapia fillets per year. ing about 75.000 chickens per day. The Other products generated by the com- organic wastes (feathers, blood, meat pany include: skins, scales, fishmeal, and chicken bones) are processed in the and fish oil. The company manages and flour plant attached to it, which has huge has the facilities for all processed prod- water consumption and related wastewa- ucts: fillet product plant, fish meal and ter treatment issues. fish oil plant. 2. Aquacorporacion de Honduras The company exports both fresh fillets and fresh gutted whole fish to the USA. Aquacorporacion de Honduras is a fully Skins and scales are also exported. integrated tilapia fish farm and process- Whole gutted whole fish, fish meal and ing facility with about 360 employees. fish oil are sold domestically. The company is located just outside of the town Rio Lindo, at the base of Also included in the infrastructure of the mountain range in which Lake Yojoa farm are basic water treatment systems resides. The farm is approximately 120 (sedimentation ponds and oxidation hectares in size. ponds) which pre-treat waste waters prior to their re-entering the natural river The production of the tilapia occurs in a systems. Probiotic products are also variety of aquaculture systems ranging regularly added to these oxidation ponds from moderate density mud bottom in order to more rapidly break down ponds to high density concrete raceways. solid waste. All facets of the tilapia life cycle are managed within the production systems, 3. Caracol Knits and Coral Knits from reproduction to market. The pro- duction facets include: reproduction, Caracol and Coral Knits are Textile larval, nursery, juvenile, and adult stages Plants Located in the municipality of
  • 8. 96 C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 Potrerillos, Cortés Honduras that started monetary information on environ- operation in 2001. The Companies are ment-related costs, earnings and known both locally and internationally savings. as a leader in the textile sector and are one of the major employers in northern Simply defined, environmental manage- Honduras. ment accounting (EMA) is management accounting (MA) with a focus on physi- The facilities include warehouses for cal information on the flow of energy, storing raw materials, finished products, water, products and materials as well as and spare parts, as well as a steam gen- monetary information on environ- eration system with boilers operated on mental costs and revenues and projects bunker and diesel fuel. The project also related to environmental protection. calls for an untreated sewage water treat- EMA is closely related to process cost- ment plant and a plant for treating do- ing as well as to environmental perform- mestic sewage and industrial wastewater ance and management systems. Well- from the dyeing process. designed and implemented EMA helps to ensure better internal management The Companies are a model in the Hon- and decision-making e.g. for investment duran textile industry that are adding appraisal, cleaner production, improving value to traditional maquila operations Eco-efficiency and calculating savings by making greater industry integration within organizations. EMA also serves and consolidation possible. as a basis for external reporting and life cycle assessments of products (1). Caracol and Coral actively take care of their environmental responsibility, Starting point for EMA is the assessment knowing that one of the biggest environ- of a material flow balance, also called mental aspects related to textile produc- mass balance or input output balance in tion is waste water treatment that comes volumes and monetary terms on the sys- from the dyeing process. The sites have tem boundary of the organization for the two Waste Water Treatment Plants, both complete previous business year, as based on activated sludge and proudly most data is available only for this sys- carries an ISO 14.001 certificate. tem boundary (7). This is especially the case for small and medium sized compa- nies (SMEs), which often don’t have EMA Methodology well developed cost accounting struc- tures. In the first step of developing the According to the definition developed material flow balance sheet, only a by the United Nations EMA Expert rough overview analysis may be per- Working Group (6), Environmental formed, instead of a detailed data collec- Management Accounting, EMA is the tion. identification, collection, analysis and use of two types of information for inter- The upcoming ISO standard on Material nal decision making: Flow Cost Accounting, ISO 14051:CD, physical information on the use, 2009 (8), defines MFCA as “a system flows and destinies of energy, water for measuring the flow and stock of ma- and materials (including wastes) and terials in processes or production lines in
  • 9. C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 97 both physical and monetary units”. All purchased materials must by MFCA is a tool for improving material physical necessity leave the com- productivity in order to reduce the rela- pany either as product or waste and tive consumption of materials, energy emission. and water and closely linked to EMA. Waste is a material which has been MFCA is regarded as an effective means purchased and paid for but which by which organizations can simultane- has not turned into a marketable ously seek environmental and economic product. benefits. MFCA improves material pro- Waste is being paid for 3 times: at ductivity in processes or production purchase, at production and for dis- lines and may consequently help reduc- posal ing related environmental impact. In Waste comprises all non-product MFCA, the flow and amount of the in- output of input materials includ- ventory of materials used within an or- ing water and energy. ganization are measured in physical units (e.g. weight, capacity, and volume) The EMA Assessment Template (in and subsequently evaluated in monetary Microsoft Excel format, available for units, which are based on the manufac- download at www.ioew.at) assists at the turing costs incurred. assessment of total annual environ- mental and material flows and related EMA places a particular emphasis on costs and provides the option to distrib- materials and related costs because (9): ute them to different cost centers, which should be equivalent to production proc- 1. the use of energy, water and materi- esses and therefore provide good quality als, as well as the generation of data for investment appraisal of specific waste and emissions, are directly processes. For material flow cost ac- related to the environmental impacts counting (MFCA) the system boundary of organizations and their products for the material flows can focus on more (10), and detailed processes within a cost centre. 2. material purchase costs and materi- als lost in waste and emissions are The EMA Excel-template consists of the most prominent cost drivers in four sheets – Mass balance, Detail, Sum many organizations. Especially in and Structure. Information is only added countries with low enforcement of into the Mass balance and the Detail legal compliance and relatively low sheet. labor costs, material and energy use and related losses are a significant The Mass balance records the physical cost driver (12). and monetary values of material inputs and product outputs in one work step, as Both, the EMA and MFCA approach these amounts should be consistent. The have the underlying assumption, that all excel template contains two columns for purchased materials must by physical the source of information for both val- necessity leave the company either as ues. The enterprise resource planning product or waste and emission. Waste is system and the accounts for materials thus a sign of inefficient production: used for production should provide this information in a consistent and detailed
  • 10. 98 C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 manner. ferred to the sheet Sum to have an over- view and a better presentation layout The actual cost assessment is performed which shows the aggregated totals by in the Detail sheet only. It can be done in cost category and calculates the costs any currency, which should be noted in into percentages to show the most rele- the heading where EURO stands in the vant environment related costs. This fig- tool. ure can also be compared to total pro- duction costs. All the cost categories are already set but the several different cost items re- The main EMA cost categories de- lated to cost accounts or taken from cost scribed in the IFAC EMA guidance centre reports should be listed with indi- document (10) are shown in Figure 1. cating the reference. The program automatically aggregates For company internal calculation of en- the costs of each cost category, but when vironmental costs, expenditures for envi- adding lines to fill in more details a last ronmental protection are only one part of cross check is recommended to make the coin. The costs of waste and emis- sure all aggregates are complete. sions include much more then the re- The sum of the costs of all categories in spective treatment facilities and disposal the sheet Detail is automatically trans- fees. Several EMA and MFCA case Material Flow related Costs 1. Materials Costs of Product Outputs 2. Materials Costs of Non-Product Outputs Environmental Protection related Cost 3. Waste and Emission Control Costs 4. Prevention and other Environmental Management Costs Figure 1: MFCA and EMA cost categories studies have shown that the costs of ronmental costs in relation to other waste disposal and emission treatment costs. However, it is not the goal to are typically 1 – 20 % of total environ- show that environmental protection is mental costs, while the purchase costs of expensive, but rather to highlight the the wasted materials represent 40 to 90 scope for savings potentials. It is also % of environmental costs, depending on not the most important task to spend a the business sector examined (13), (14), lot of time defining exactly which costs (15) . are environmental or not, or what per- centage of something is environmental Adding the purchase value of non- or not, or if Energy belongs to NPO and product output to the corporate environ- to what degree. Environmental protec- mental costs increases the share of envi- tion projects not only have effects on
  • 11. C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 99 Environmental protection expenditure (emissions treatment, control and waste pre- vention costs) + Costs of Non Product Output (Costs of unproductive material, capital, and personnel) = Total corporate environment related costs Figure 2: Total corporate environment related costs nature, but also on neighbors (noise, In other words, corporate environmental odors, pollution) and employees (health and material flow costs are just a subset and safety), if related to material and of the bigger cost universe that is neces- energy flows. In addition they result in a sary for good decision-making. Environ- reduction of risks for employees, nature mental costs are part of an integrated and neighbors in case of accidents and system of materials, energy and money other occasional production events. flows through a corporation, and not a separate type of cost. Doing EMA and It is often difficult to determine the envi- MFCA is simply doing better, more ronmental portion of these costs. As comprehensive Management Account- with integrated cleaner technologies that ing, while wearing an environmental hat are often more cost and material effi- that opens the eyes to hidden costs. cient, the environmental portion of Therefore, the focus of MFCA is no health and safety or risk prevention ac- longer on assessing total environmental tivities usually cannot be determined costs, but on a revised calculation of precisely. In general, it may be stated production costs on the basis of material that assets that are allotted 100% to the flows (including energy and water). environment are bad for the environment as they are often end-of-pipe technolo- gies that do not solve the problem at the Results of the EMA assessments source, but rather shift it from one envi- ronmental medium to another (e.g. from Starting point of an EMA project is put- the air to the soil and then into the wa- ting the right team members together. ter). These approaches are expensive Experience shows that the environ- and inefficient. mental manager barely has access to the actual cost accounting documents of the The most important task is to make sure company and only is aware of a tiny that ALL relevant and significant costs fraction of aggregate environmental are considered when making business costs. On the other hand, the financial decisions. This is why Figure 2 calls the accountant/controller does have most of total sum: total environment related the information but is unable to separate costs. This is the universe of costs, that the environmental part without further the environmental manager deals with guidance. In addition, he or she is lim- and that can possibly be reduced by pol- ited to thinking within the framework of lution prevention and material and en- existing accounts. Also, the two depart- ergy efficiency projects. ments tend to have a severe language problem.
  • 12. 100 C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 So combining the competencies for Using the explanations of the EMA monetary accounting and process engi- books and the Excel Template provided neering/environmental management and with it, the first EMA assessment for the gaining support from both sides is vital previous business year for any given for the success of any EMA project. company should not take longer than a 1 to 2 days workshop with the accountant Another important guideline on the way and process engineer. is to focus the assessments on what is easily available from existing records The cost assessment reveals improve- and to note, where improvements to the ment options in two areas: information system would be recom- 1. What always can be found, are op- mended, so that future assessments will tions and measures necessary to provide better data in shorter time. It is improve the quality and consistency NOT the goal of an EMA assessment to of data and information flows in an come up with “complete data” for the organisation. This is the starting past and spend a lot of time tracing old point of EMA most projects and the invoices. It is rather the goal to open the focus of most follow up projects. eye for improvement necessities and develop an overview on the most signifi- 2. In companies, that have not done cant material flows and related costs. environmental management pro- jects for several years, also techni- The resulting recommendation for the cal improvement options may im- assessment is: don’t be shy to use esti- mediately become obvious. What mates! The people at the production always is made visible, mostly for processes often can provide very good the first time, are the costs related estimates for loss percentages, which are to inefficient production, wasting much more accurate than the figures materials and energy. So even if the used in the cost accounting department. technical solution might not be Estimates can at a later stage be im- known at the end of the first assess- proved by more detailed measurements, ment, the priority areas for deeper but for the first assessment don’t worry investigation will have been de- not to be perfect. It is better to have an fined and the total range of environ- estimate than no figure. But the calcula- ment related costs will be clearer. tion procedure or the information source for the estimate should be recorded. The following table shows an aggre- gated result of the 2 companies in Hon- The goal of the first assessment is to duras from the food industry. As both be able to present the entire material companies have not installed an environ- inputs and total environmental costs mental management system yet, their of the previous business year to top costs relating to environmental protec- management, and tion are negligible (2 % for end of pipe come up with improvement recom- treatment, most related with the waste mendations and water treatment plant and 0,2 % for in- gain support to improve the infor- ternal personal dealing with pollution mation system and technical proc- prevention). In all the EMA case studies, esses. the actual costs are subject to secrecy.
  • 13. C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 101 Figure 3: Average cost distribution in the food industry in the Honduras case studies Environment related costs by environ- Air and Water and Solid Waste General Total in % mental domains and cost categories climate Waste environ- Water mental Manage- ment 1. MATERIALS COSTS OF NON- 20,0% 2,4% 75,3% 0,0% 97,7% PRODUCT OUTPUTS 1.1. Raw and Auxiliary Materials 0,0% 0,0% 70,0% 0,0% 70,0% 1.2. Packaging Materials 0,0% 0,0% 0,1% 0,0% 0,1% 1.4. Operating Materials 0,0% 2,4% 4,7% 0,0% 7,1% 1.5. Water 0,0% 0,0% 0,0% 0,0% 0,0% 1.6. Energy 20,0% 0,0% 0,0% 0,0% 20,0% 1.7. Processing Costs 0,0% 0,0% 0,5% 0,0% 0,5% 2. END-OF-PIPE 0,0% 1,6% 0,2% 0,2% 2,0% 2.1. Equipment Depreciation 0,0% 0,4% 0,0% 0,2% 0,6% 2.2. Operating Materials 0,0% 0,4% 0,0% 0,0% 0,4% 2.3. Water and Energy 0,0% 0,0% 0,0% 0,0% 0,0% 2.4. Internal Personnel 0,0% 0,4% 0,1% 0,0% 0,5% 2.5. External Services 0,0% 0,3% 0,0% 0,0% 0,3% 2.6. Fees, Taxes and Permits 0,0% 0,1% 0,1% 0,0% 0,2% 2.7. Insurance 0,0% 0,0% 0,0% 0,0% 0,0% 2.8. Remediation and Compensation 0,0% 0,0% 0,0% 0,0% 0,0% 3. INTEGRATED PREVENTION 0,0% 0,0% 0,1% 0,1% 0,2% 3.1. Equipment Depreciation 0,0% 0,0% 0,0% 0,0% 0,0% 3.2. Operating Materials, Water, Energy 0,0% 0,0% 0,0% 0,0% 0,0% 3.3. Internal Personnel 0,0% 0,0% 0,1% 0,1% 0,2% 3.4. External Services 0,0% 0,0% 0,0% 0,0% 0,0% 3.5. Other 0,0% 0,0% 0,0% 0,0% 0,0% 4. RESEARCH and DEVELOPMENT 0,0% 0,0% 0,0% 0,0% 0,0% COSTS 5. FINES 0,0% 0,2% 0,0% 0,0% 0,2% TOTAL ENVIRONMENT-RELATED COSTS (1. + 2. + 3. + 4. + 5. + 6.) 20,0% 4,2% 75,6% 0,3% 100,1% 7. ENVIRONMENT-RELATED EARNINGS 7.1. Other Earnings 0,0% 0,0% -0,1% 0,0% -0,1% 7.2. Subsidies 0,0% 0,0% 0,0% 0,0% 0,0% TOTAL ENVIRONMENT-RELATED EARNINGS 0,0% 0,0% -0,1% 0,0% -0,1% TOTAL ENVIRONMENT-RELATED COSTS & EARNINGS 20,0% 4,2% 75,5% 0,3% 100,0%
  • 14. 102 C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 Therefore the table shows the average Jasch C., (2009) “Environmental and percentage distribution, which allows Material Flow Cost Accounting - interpretation of the most significant Principles and Procedures”, Eco- cost carriers. Efficiency in Industry and Sci- ence, Vol. 25, Vienna: Institut für As energy is not regarded as a product in Ökologische Wirtschaftsfor- the food industry, the 20 % costs for en- schung. ergy can be taken as a reference point. Jasch Ch., (2006) “How to perform an The by far most significant costs are re- environmental cost assessment in lated to the loss of raw and auxiliary one day”, Journal of Cleaner Pro- materials, which are not processed into a duction, Vol. 14, No 14. marketable product. They account for 70 Thrane M., Nielsen E., Christensen P., % of the total environment related costs. (2009) “Cleaner Production in Even though part of the skin, blood, etc. Danish fsih processing – experi- are being processes into animals feed, ences, status and possible future the related income of 0,1 % is negligible strategies”, Journal of cleaner Pro- in relation to the material input costs duction, Vol. 17, No 3, pp. 380 – lost. Any improvement of the raw mate- 390. rial processing efficiency would thus United Nations Division for sustainable significantly reduce costs and environ- Development, “Department of mental impact, as most of the organic Economic and Social Affairs”, waste ends up in the wastewater stream. Environmental Management Ac- However, both companies neither moni- counting, Procedures and Princi- tor the actual volumes of organic waste ples, (United Nations publication, being processed in the animal feed plant Sales No. 01.II.A.3), www.un.org/ nor the waste volumes discharged into e s a/ s us t d e v/ e s t e ma 1. ht m , the river. www.ioew.at Jasch Ch., (2003) “The use of environ- By installing an environmental manage- mental management accounting ment system the costs for internal and (EMA) for identifying environ- external people working on integrated mental costs”, Journal of Cleaner prevention will go up. At the same time Production, Vol. 11, September. they would be working on reducing the ISO (2009) “ISO:CD 14051, Material material costs of non-product outputs. Flow Cost Accounting, Geneva: Case studies in Austria from the brewery International Organization for industry have seen a reduction in the Standardization. relative costs of non-product outputs to Jasch Ch., (2006) “Environmental man- as low as 55 %. agement accounting (EMA) as the References next step in the evolution of man- agement accounting”, Journal of UNIDO (2010) http://www.unido.org/ Cleaner Production, Vol. 14, No. index.php?id=o5151, 13.3.2010 14. ISO (2001) ISO 14001, Environmental Schaltegger S, Burritt R. (2000) Con- Management System Specifica- temporary Environmental Ac- tion, Geneva: International Or- counting – Issues, Concepts and ganization for Standardization.
  • 15. C. Jasch, D. Ayres, L. Bernaudat / Issues in Social and Environmental Accounting 2 (2010) 89-103 103 Practice. UK: Greenleaf Publish- menting Environmental Manage- ing. ment Accounting: Status and Burritt R, Hahn T, Schaltegger S. (2002) Challenges, Dordrecht, NL: Klu- “Towards a Comprehensive wer Academic Publ. Framework for Environmental K. Fichter, T. Loew and E. Seidel, Management Accounting – Links (1997) Betriebliche Between Business Actors and Umweltkostenrechung (available EMA Tools”, Australian Account- only in German). Berlin: Springer ing Review, Vol. 12, No. 2, pp. 39 Verlag. -50. K. Fichter, T. Loew, C. Redmann and IFAC (2005) Environmental Manage- M. Strobel, (1999) ment Accounting, International Flusskostenmanagement, Guidance document, New York: Kostensenkung und Öko- International Federation of Ac- Effizienz durch eine countants. Materialflußorientierung in der Jasch Ch., Danse M., (2005) Kostenrechnung (available only in “Environmental Management Ac- German). Wiesbaden, Germany: counting pilot projects in Costa Hessisches Ministerium für Rica”, in Bennet M., Rikhardson Wirtschaft, Verkehr, und P., Schaltegger S. (Eds.) Imple- Landesentwicklung.
  • 16. International Journals Call for Paper The IISTE, a U.S. publisher, is currently hosting the academic journals listed below. The peer review process of the following journals usually takes LESS THAN 14 business days and IISTE usually publishes a qualified article within 30 days. Authors should send their full paper to the following email address. More information can be found in the IISTE website : www.iiste.org Business, Economics, Finance and Management PAPER SUBMISSION EMAIL European Journal of Business and Management EJBM@iiste.org Research Journal of Finance and Accounting RJFA@iiste.org Journal of Economics and Sustainable Development JESD@iiste.org Information and Knowledge Management IKM@iiste.org Developing Country Studies DCS@iiste.org Industrial Engineering Letters IEL@iiste.org Physical Sciences, Mathematics and Chemistry PAPER SUBMISSION EMAIL Journal of Natural Sciences Research JNSR@iiste.org Chemistry and Materials Research CMR@iiste.org Mathematical Theory and Modeling MTM@iiste.org Advances in Physics Theories and Applications APTA@iiste.org Chemical and Process Engineering Research CPER@iiste.org Engineering, Technology and Systems PAPER SUBMISSION EMAIL Computer Engineering and Intelligent Systems CEIS@iiste.org Innovative Systems Design and Engineering ISDE@iiste.org Journal of Energy Technologies and Policy JETP@iiste.org Information and Knowledge Management IKM@iiste.org Control Theory and Informatics CTI@iiste.org Journal of Information Engineering and Applications JIEA@iiste.org Industrial Engineering Letters IEL@iiste.org Network and Complex Systems NCS@iiste.org Environment, Civil, Materials Sciences PAPER SUBMISSION EMAIL Journal of Environment and Earth Science JEES@iiste.org Civil and Environmental Research CER@iiste.org Journal of Natural Sciences Research JNSR@iiste.org Civil and Environmental Research CER@iiste.org Life Science, Food and Medical Sciences PAPER SUBMISSION EMAIL Journal of Natural Sciences Research JNSR@iiste.org Journal of Biology, Agriculture and Healthcare JBAH@iiste.org Food Science and Quality Management FSQM@iiste.org Chemistry and Materials Research CMR@iiste.org Education, and other Social Sciences PAPER SUBMISSION EMAIL Journal of Education and Practice JEP@iiste.org Journal of Law, Policy and Globalization JLPG@iiste.org Global knowledge sharing: New Media and Mass Communication NMMC@iiste.org EBSCO, Index Copernicus, Ulrich's Journal of Energy Technologies and Policy JETP@iiste.org Periodicals Directory, JournalTOCS, PKP Historical Research Letter HRL@iiste.org Open Archives Harvester, Bielefeld Academic Search Engine, Elektronische Public Policy and Administration Research PPAR@iiste.org Zeitschriftenbibliothek EZB, Open J-Gate, International Affairs and Global Strategy IAGS@iiste.org OCLC WorldCat, Universe Digtial Library , Research on Humanities and Social Sciences RHSS@iiste.org NewJour, Google Scholar. Developing Country Studies DCS@iiste.org IISTE is member of CrossRef. All journals Arts and Design Studies ADS@iiste.org have high IC Impact Factor Values (ICV).