Keywords summaries 2009.

Contenuti dei seminari 2009.

Fire effects, Air Pollution, GMO, IAS, biodiversity, BAT.


Effetti degli incendi, Inquinamento Atmosferico, Organismi Geneticamente Modificati, Specie Aliene Invasive, Biodiversità, Migliori Tecniche Disponibili.
 
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Summaries Feb 2009

1. Fire Effects on Soils and restoration strategies


The seminar showed us the great fire problems of many of Portuguese regions, focusing on great fires occurring during the second part of 20th century. All them have a deep effect on soil moisture and water repellence.

Infact the first stress is on the objectives of the research , to put in better conditions all the area affected by fire, both wild and regulated.

Than the research found many study site in Portugal affected by fire more than other: the north and green mountains and the coast, and the southern-west coast.

The methodology used for restore those affected site is mainly to manage new plantation and to measure soli water repellence.

Fire could affect, infact, soil water repellence, that increase and could have not only direct effect on soil, but also offsite effect such as covering by ash or dust of nearby reservoir, great water flow and covering settlements.

There are a large nutrients loss after fire, so the first recover tried was to cover the soil with chopped balk or stems and branches, but, even if the soil water repellence comes better, it doesn’t return as it was before the fire.

Were presented two project, one for recovering and one for mitigation, called RECOVER project and DESIRE project.

The second project will begin by making an inventory of local knowledge. Working with local residents, the scientists will study the methods and techniques used to prevent land degradation in that region and combine them with new scientific insights.

The researchers hope that this close collaboration of scientists with local stakeholder groups will lead to acceptable and feasible conservation techniques.

Ultimately, the DESIRE project should lead to practical guidelines for responsible land use.

That could lead to a number of recommendations to mitigate fire, prevention is the great goal over all.

That seminar is very interesting because stress the attention on general fire problems, such we have in our Sardinia Island, I think it could be used also Satellite Remote Sensing (like I am using in my research for other kind) to evaluate some soil index and also to search for fire spot.

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2. Study of aqueous electrolytic solutions with high concentration

CuSO4-H2SO4-H2O


The goal of the study is a good model for electrolytic solutions of that kind:

- a mix of electrolytic;

- a mix of complex and solid solutions ;

- a great range of electrolytic concentrations, with different limits for

- acid-> H2O free (2 mol H2O/ 1 mole AS)

- salt -> saturation of solutions

After that there is the application of a model for acid sulphuric solutions and metallic ions in order to achieve a good knowledge, or to give a contribute, of those electrolytic solutions, calculating or evaluating the thermodynamic balance and parametric constances.

Those kind of solutions are very important in industry, for the production of acids, hydrometallurgy of metallic minerals, batteries and for drying different aliments.

Inside an aqueous solution the sulphuric acid play as a string acid and give birth to ions H2SO4 and SO4. many studies show that the first dissociation of sulphuric acid became complete for measures of H2SO4 less than 40 mol/kg (or 14 mol/ l).

Many studies were done on the presence of ions HSO4, SO4 and H and the measure of their concentrations. The concentration of ions H was calculated indirectly from the concentration of ions SO4 and HSO4, when the neutrality of the solution is achieved.

The modelling of aqueous mixtures of a bivalent metal sulphate and sulphuric acid according to the treatment of Pitzer is complicated by the formation of bisulphate ion and by the need to include the effects of unsymmetrical mixing of ions of like but unequal charge. Because of the economic importance of the recovery of copper by the leaching of its ores with sulphuric acid, it is especially important to improve estimates of Pitzer parameters for the CuSO4-H2SO4-H2O system.

The conclusion is that the model for high electrolytic concentration in aqueous solutions is independent of the mix, like acid sulphuric and independent of the salt used, like copper sulphate. This method could be used for calculate other properties of the chemical system or to predict the behaviour of other acid and metallic ions or salt.

That seminar is very far from my research, because stress the attention on general chemistry model of aqueous electrolytic solutions and my research is for Satellite Remote Sensing for atmospheric application.

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Summaries Sep 2009


  1. Explain how does the phenomenon of « greenhouse effect » occur?

The Earth receives energy from the Sun mostly in the form of visible light; about 50% of the sun's energy reaches the Earth and is absorbed by the surface. Like all bodies with a temperature of nearly 300 K, the Earth's surface radiates energy in the infrared range. Greenhouse gases ( GHG ) absorb infrared radiation and pass the absorbed heat to other atmospheric gases through molecular collisions. The GHG also radiate in the infrared range. Radiation is emitted both upward, with part escaping to space, and downward toward Earth's surface. The surface and lower atmosphere are warmed by the part of the energy that is radiated downward, making our life on earth possible. In order, Earth's most abundant GHG are water vapor, carbon dioxide, methane, nitrous oxide, ozone and CFCs. Their contribution to the greenhouse effect: water vapor, which contributes 36–70% ; carbon dioxide, which contributes 9–26% ; methane, which contributes 4–9% ; ozone, which contributes 3–7%. The major non-gas contributor to the Earth's greenhouse effect, clouds, also absorb and emit infrared radiation and thus have an effect on radiative properties of the atmosphere. The list of the main GHG made by the IPCC is CO2, CH4, N2O, Ccl2F2, CF4 and SF6, but I will discuss later on question 3 about them.

The term 'greenhouse effect' originally came from the greenhouses used for gardening, but as mentioned the mechanism for greenhouses operates differently. Many sources make the "heat trapping" analogy of how a greenhouse limits convection to how the atmosphere performs a similar function through the different mechanism of infrared absorbing gases. A greenhouse is usually built of glass, plastic, or a plastic-type material. It heats up mainly because the sun warms the ground inside it, which then warms the air in the greenhouse. The air continues to heat because it is confined within the greenhouse, unlike the environment outside the greenhouse where warm air near the surface rises and mixes with cooler air aloft. This can be demonstrated by opening a small window near the roof of a greenhouse: the temperature will drop considerably. Greenhouses thus work primarily by preventing convection; the atmospheric greenhouse effect however reduces radiation loss, not convection.

  1. How can the ozone layer be destructed?

The overall amount of O3 in the stratosphere is determined by a balance between photochemical production and recombination of O and O2. Ozone can be destroyed by a number of free radical catalysts, the most important of which are the radicals OH-, the NO- and atomic Cl and Br. All of these have both natural and anthropogenic sources; at the present time, most of the radicals in the stratosphere are of natural origin, but human activity has dramatically increased the levels of chlorine and bromine. These elements are found in certain stable organic compounds, especially the altready mentioned for the greenhouse effect, CFCs, which may find their way to the stratosphere without being destroyed in the troposphere due to their low reactivity. Once in the stratosphere, the Cl and Br atoms are liberated from the parent compounds by the action of ultraviolet light. Now the O3 depletion is stabilized.

  1. What is GWP of a given gas? What is the lifetime basis for the calculation of GWP? List the values of the 6 main GHG (you may use the IPCC website).

Every greenhouse gases have a Global Warming Potential Index, named GWP, here below the table of the 6 main GHG with the corresponding GWP index, by the IPCC, Intergovernmental Panel on Climate Change web site or as given during the seminar in Chia:

Gas

CO2

CH4

N2O

CCl2F2

CF4

SF6

GWP Index

1

21

310

6200

6500

23900



GWP is a measure of how much a given mass of GHG is estimated to contribute to.Global Warming ( GW ). It is a relative scale which compares the gas in question to that of the same mass of CO2. A GWP is calculated over a specific time interval and the value of this must be stated whenever a GWP is quoted or else the value is meaningless. The substances subject to restrictions in the Kyoto Protocol either are rapidly increasing their concentrations in Earth's atmosphere or have a large GWP. The GWP depends on the following factors: the absorption of infrared radiation by a given species ;the spectral location of its absorbing wavelengths ; the atmospheric lifetime of the species. So a substance's GWP depends on the timespan over which the potential is calculated. A gas which is quickly removed from the atmosphere may initially have a large effect but for longer time periods as it has been removed becomes less important. Thus methane has a potential of 21 over 100 years but more over 20 years; conversely SF6 has a GWP of 23900 over 100 years but less over 20 years. The GWP value depends on how the gas concentration decays over time in the atmosphere. This is often not precisely known and hence the values should not be considered exact. For this reason when quoting a GWP it is important to give a reference to the calculation. The GWP for a mixture of gases can not be determined from the GWP of the constituent gases by any form of simple linear addition. Commonly, a time horizon of 100 years is used by regulators.

  1. What are the main resolutions of the KP at COP 3 and what are the decisions made in COP7 for the implementation of the commitments made to reduce GHG emissions?

The Kyoto Protocol is an international agreement linked to the United Nations Framework Convention on Climate Change. The major feature of the Kyoto Protocol is that it sets binding targets for 37 industrialized countries and the European community for reducing GHG emissions .These amount to an average of 5% against 1990 levels over the five-year period 2008-2012. The text of the Protocol to the UNFCCC (United Nations Framework Convention on Climate Change) was adopted at the third session of the Conference of the Parties (COP 3) in Kyoto, Japan, on 11 December 1997; it was open for signature from 16 March 1998 to 15 March 1999 at United Nations Headquarters, New York. By that date the Protocol had received 84 signatures. Those Parties that have not yet signed the Kyoto Protocol may accede to it at any time. The Protocol is subject to ratification, acceptance, approval or accession by Parties to the Convention. It entered into force on 16 February 2005 - the ninetieth day after at least 55 Parties to the Convention, incorporating Annex I Parties which accounted in total for at least 55 % of the total carbon dioxide emissions for 1990 from that group - deposited their instruments of ratification, acceptance, approval or accession. Under the Treaty, countries must meet their targets primarily through national measures. However, the Kyoto Protocol offers them an additional means of meeting their targets by way of three market-based mechanisms: emission trading– known as “the carbon market"; clean developed mechanism (CDM); joint implementation (JI). The mechanisms help stimulate green investment and help Parties meet their emission targets in a cost-effective way. The major distinction between the Protocol and the Convention is that while the Convention encouraged industrialised countries to stabilize GHG emissions, the Protocol commits them to do so. Recognizing that developed countries are principally responsible for the current high levels of GHG emissions in the atmosphere as a result of more than 150 years of industrial activity, the Protocol places a heavier burden on developed nations under the principle of “common but differentiated responsibilities.”

At the COP 7 meeting in Marrakech 2001, negotiators in effect completed the work of the Buenos Aires Plan of Action, finalizing most of the operational details and setting the stage for nations to ratify the Protocol. The completed package of decisions are known as the Marrakech Accords. The United States delegation continued to act as observers, declining to participate in active negotiations. Other parties continued to express their hope that the United States would re-engage in the process at some point, but indicated their intention to seek ratification of the requisite number of countries to bring the Protocol into force (55 countries representing 55% of developed country emissions of carbon dioxide in 1990). The main decisions at COP 7 included: Operational rules for international emissions trading among parties to the Protocol and for the CDM and joint implementation; a compliance regime that outlines consequences for failure to meet emissions targets but defers to the parties to the Protocol after it is in force to decide whether these consequences are legally binding; accounting procedures for the flexibility mechanisms.

  1. Can you give the main requirements that a PDD of a CDM project must contain to be accepted by the executive board of CDM of the UN?

The Clean Developed Mechanism (CDM) is a project-based mechanism under the KP to the UNFCCC that enables the generation and issuance of certified emission reductions (CERs) from eligible CDM project activities. The project design document (PDD) is the key document involved in the validation and registration of a CDM project activity. It is one of the three documents required for a CDM project to be registered, along with the validation report from the Designated Operational Entity (DOE) and the letter of approval from the Designated National Authority (DNA).

Project activities under the CDM must be:

  1. hosted by non-Annex I Parties (host parties) that have ratified the Kyoto Protocol and established a DNA;

  2. developed by public or private entities authorised by the relevant host Party and Annex I parties involved in the project activity;

  3. validated by a DOE in accordance with the CDM project eligibility and participation requirements, including the use of an approved baseline and monitoring methodology;

  4. registered by the CDM Executive Board after review by a Registration and Issuance Team to ensure compliance with the international rules;

  5. and once commissioned and operational, verified and certified by a DOE as resulting in real, additional, measurable and verifiable reductions in greenhouse gas emissions below an approved business as usual baseline scenario.

CERs issued by the Executive Board are sold and purchased under private commercial arrangements between the project participants for the sale and purchase of the CERs and forwarded and transferred between Annex I Parties - and the public and private entities authorised by those Parties - via the international translation log (ITL), established under the international emissions trading mechanism of the Kyoto Protocol. CERs can then be used along side other Kyoto credits to satisfy Parties' legally binding quantified emission limitation and reduction commitments (often referred to as 'Kyoto targets').

In summary, the PDD: the document describes the project and establish boundaries, baseline methodology, duration and crediting period of the project. But also PDD describes how the project is additional (additionality is the requirement that the greenhouse gas emissions after implementation of a CDM project activity are lower than those that would have occurred in the most plausible alternative scenario to the implementation of the CDM project activity) and what are its environmental impacts, provides information on the sources of public funding for the project, summarises stakeholder comments and describes the monitoring plan setting out all relevant calculations.

  1. What is the meaning of “baseline” in a CDM project?

The baseline for a CDM project activity is the scenario that reasonably represents the anthropogenic emissions by sources of greenhouse gases that would occur in the absence of the proposed project activity. In other words, a baseline for a CDM project activity is a hypothetical reference case, representing the volume of greenhouse gases that would have been emitted if the project were not implemented. Therefore, the baseline can be used to determine: whether a CDM project activity is additional and the volume of additional greenhouse gas emission reductions achieved by a project activity. Baselines must cover emissions from all gases, sectors and source categories listed in Annex A to the KP that occur within the project boundary.

  1. Can you think of two different projects that can be considered as CDM projects (each project should be explained in two or three sentences)?

  1. Biomass Electricity Generation Project: a) The project activity is a renewable energy project which consists of the construction and operation of a biomass generation plant that will generate electricity of about 10 MW required by Celulose ((C6H10O5)n) in the paper manufacturing process; b) the proposed project activity involves displacing more carbon-intensive electricity from the grid with electricity generated by a GHG-neutral option; c) the project activity also involves methane avoided from biomass not being landfilled.

  2. River Hydroelectric Plant Project: a) the purpose of this project is to generate electricity with renewable water sources, and to displace part of the electricity from fossil fuel-fired plants connected to the used grid. The hydropower system use water at a rate no greater than that which runs down the river and will provide electricity of 6 MW; b) the estimated annual GHG emission reductions are 8 tCO2e by the project; c) reduction of other environmental pollutants such as SO2, NOx, and dust derived from fossil fuel-fired plants;e) the project activity will contribute to sustainable development by the use of renewable hydro resources available in the region and the creation of local employment opportunities during the construction and operating phases.

  1. By consulting the website of the UNFCCC, how many CDM projects have been registered and how many are in the pipeline “being under review” up to the day you are answering this question? How many CERs can we gain from these projects?

Data of 13 sep 2009.

CDM project pipeline: > 4200, of which 1809 are registered and 80 are requesting registration.

From the 1809 CDM project registered the annual average number of CERs is 313,221,783. and the expected CERs until the end of 2012 will be > 2,900,000,000 for the entire CDM pipeline, > 1,640,000,000 for the already registered CDM projects and > 30,000,000 for the last 80 requesting registration CDM projects.

  1. What is the definition of “Emission Factor” in a CDM electricity generation project?

For the purpose of determining the electricity emission factors, a project electricity system is defined by the spatial extent of the power plants that are physically connected through transmission and distribution lines to the project activity (e.g. the renewable power plant location or the consumers where electricity is being saved) and that can be dispatched without significant transmission constraints. First some definitions:

Power plant/unit. A power plant / unit is a facility for the generation of electric power. Several power units at one site comprise one power plant, whereby a power unit characterizes that it can be operated independently of the other power units at the same site. Where several identical power units are installed at one site, they may be considered as one single power unit.

Net electricity generation refers to the difference between the total quantity of electricity generated by the power plant / unit and the auxiliary electricity consumption of the power plant / unit.

Grid/project electricity system is defined by the spatial extent of the power plants that are physically connected through transmission and distribution lines to the project activity (e.g. the renewable power plant location or the consumers where electricity is being saved) and that can be dispatched without significant transmission constraints.

For the purpose of determining the build margin emission factor, the spatial extent is limited to the project electricity system, except where recent or likely future additions to transmission capacity enable significant increases in imported electricity. In such cases, the transmission capacity may be considered a build margin source.

For the purpose of determining the operating margin emission factor, use one of the following options to determine the CO2 emission factor(s) for net electricity imports (EFgrid,import,y) from a connected electricity system within the same host country(ies):

(a) 0 tCO2/MWh, or

(b) The weighted average operating margin (OM) emission rate of the exporting grid, or

(c) The simple operating margin emission rate of the exporting grid, determined as described in step; or (d) The simple adjusted operating margin emission rate of the exporting grid.

The simple OM emission factor is calculated as the generation-weighted average CO2 emissions per unit net electricity generation (tCO2/MWh) of all generating power plants serving the system, not including low-cost / must-run power plants / units. It may be calculated:

Based on data on fuel consumption and net electricity generation of each power plant / unit (Option A), or

Based on data on net electricity generation, the average efficiency of each power unit and the fuel

type(s) used in each power unit (Option B), or

Based on data on the total net electricity generation of all power plants serving the system and the fuel types and total fuel consumption of the project electricity system (option C)

Option A should be preferred and must be used if fuel consumption data is available for each power plant / unit. In other cases, option B or option C can be used. For the purpose of calculating the simple OM,

Option C should only be used if the necessary data for option A and option B is not available and can only be used if only nuclear and renewable power generation are considered as low-cost / must-run power sources and if the quantity of electricity supplied to the grid by these sources is known.

Baseline emissions (BE) are calculated by multiplying the electricity generated in the project plant (EG) with a baseline CO2 emission factor (EF), as follows:

BEy = EGy * EFy

Where:

BEy Baseline emissions in year y (tCO2)

EG,y Quantity of electricity generated in the project plant in year y (MWh)

EFy Baseline emission factor in year y (tCO2/MWh)

  1. By reading this internet article (http://news.yahoo.com/s/ap/climate_09_greenland_s_melt) and from your general knowledge, what would happen (all possible impacts) in about 50 years if we do nothing about climate change and global warming?

No one can say with certainty whether that will take 50 years or 100, or 1,000. But, reading the article in a BAU scenario, if we do nothing, the global warming will really increase and so for the air mean temperature (+ 2°C), the ocean current of warmer water, the depletion of glaciers (that could also collapses at least) and so the sea level ( +10 – +30 cm) and the El Nigno System, there will be also more random cataclysmic weather effects.

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  1. What is the trend in invasive alien species (IAS)?

The definition of IAS express the phrase in terms of non indigenous species ( plants or animals) that adversely affect the habitats they invade economically, environmentally or ecologically. An introduced species might become invasive if it can out-compete native species for resources such as nutrients, light, physical space, water or food. If these species evolved under great competitions or predation, the new environment may allow them to proliferate quickly. Ecosystems in which all available resources are being used to their fullest capacity by native species can be modeled as zero sum systems, where any gain for the invader is a loss for the native. However, such unilateral competitive superiority (and extinction of native species with increased populations of the invader) is not the rule. Invasive species often coexist with native species for an extended time, and gradually the superior competitive ability of an invasive species becomes apparent as its population grows larger and denser and it adapts to its new location.

In the Millenium Ecosystem Assessment Report, IAS is globally the second major threat to biodiversity, and it is also fast growing.


  1. How are IAS introduced?

Trade, turism and transport (either by land transport and shipping) of goods across borders accelerate the spread of alien species. In Europe the main introduction' ways of IAS are: Suez and Gibraltar, almost 38%; Ships, 25%; Aquaculture, 20%; then also Aquaturism, turism and trade.



  1. What are the impacts of IAS?

Altought the Biodiversity loss is the most evident impact, there are some others of different types: environmental and ecological, but also economical.

Biological species invasions alter ecosystems in a multitude of ways.

While all species compete to survive, invasive alien species appear to have specific traits or combinations of specific traits that allow them to outcompete endemyc species. Sometimes they just have the ability to grow and reproduce more rapidly than native species; other times it's more complex, involving a lot of mixed traits and interactions.

As highly adaptable and generalized species are introduced to environments already impacted by human activities, some native species may be put at a disadvantage to survive while other species survival is enhanced.

Invasive species can change the functions of ecosystems. For example invasive plants can alter the fire regime, nutrient cycling, and hydrology in native ecosystems. Invasive species that are closely related with rare native species have the potential to hybridize with the native species. Harmful effects of hybridization have led to a decline and even extinction of native species.

The unintentional introduction of forest pest species and plant pathogens can change forest ecology and negatively impact timber industry.

An increasing threat of exotic diseases exists because of increased transportation and encroachment of humans into previously remote ecosystems (think about the asian tiger mosquitos that is only one example).

Economic costs from invasive species can be separated into direct costs through production loss in agriculture and forestry, and management costs of invasive species. In addition to these costs, economic losses can occur through loss of recreational and tourism revenues. Economic costs of invasions, when calculated as production loss and management costs, are low because they do not usually consider environmental damages. If monetary values could be assigned to the extinction of species, loss in biodiversity, and loss of ecosystem services, costs from impacts of invasive species would drastically increase.

So native species seems to be vulnerable, especially islands species.

And to prevent biodiversity the impact of IAS costs money. In Europe is estimate 12,7billion € per year.


  1. What are some ways to address the problem of IAS?

The strategies and guidelines given by the Convention on Biological Diversity aim governments and state that: "Each Contracting Party shall, as far as possible and as appropriate, prevent the introduction of, control or eradicate those alien species which threaten ecosystems, habitats or species”.

Early detection and constant monitoring is vital to save endemyc species.

Parallel to the development of the strategy, priority interventions at the site level will be implemented, like:

  • To increase awareness of invasive alien species as a major issue affecting native biodiversity and ecosystems.

  • To encourage necessary research and the development and sharing of an adequate knowledge base to address the problem of invasive alien species.

  • To encourage prevention of invasive alien species introductions as a priority issue requiring regional, national and site level actions.

  • To minimise the number of unintentional introductions and to prevent unauthorised introductions of alien species.

  • To ensure that intentional introductions, including those for biological control purposes, are properly evaluated in advance, with full regard to potential impacts on biodiversity.

  • To encourage the development and implementation of eradication and control campaigns and programmes for invasive alien species, and to increase the effectiveness of those campaigns and programmes.

  • To encourage the development of a comprehensive framework for national legislation and international cooperation to regulate the introduction of alien species as well as the eradication and control of invasive alien species.


  1. What are ecosystem services and how do they affect human well being?

Ecosystem services are defined as the products of ecological functions or processes that directly or indirectly contribute to human well-being, or have the potential to do so in the future. The Millennium Ecosystem Assessment (MA) defines ecosystem services as the benefits people derive from ecosystems. These include provisioning services such as food and water; regulating services such as regulation of floods, drought, land degradation, and disease; supporting services such as soil formation and nutrient cycling; and cultural services such as recreational, spiritual, religious and other nonmaterial benefits.

The well-being should be understood as “state of happiness, good health and/or prosperity” whereas quality if life is the degree of well-being felt by an individual or group of people. It consists of two components: physical and psychological. The physical aspect includes such things as health, diet, and protection against pain and disease. The psychological aspect includes stress, worry, pleasure and other positive or negative emotional states.

There are several key components of human well-being:

  • the basic material needs for a good life,

  • health,

  • good social relations,

  • and personal security,

  • freedom of choice and action

The Millennium Ecosystem Assessment aims at identification of direct and indirect ways the change in ecosystem condition can affect the human well-being positively or negatively. The problem is more complicated if one starts to think how multidimensional well-being is and therefore how hard it is to measure it. However, number of indices have been developed dealing with assessing human well-being at different scales (some examples: Human Development Index HDI, Happy Planet Index HPI, US Well Being Index).


  1. Name some financial and non-financial measures to pay for Nature.

Financial

How to make Biodiversity an economic and financial value? It is a good task. First we have to list some benefits of a preserved ecosystem and then associate a value with changes of those benefits (food, water, climate regulation, medicines, recreations and so on).

So a financial measure could be a payment to landowners in order to manage their lands to support ecosystems and not to build houses or to establish a new agriculture or aquaculture. Also the idea to apply fees, taxes or fines, to discourage activites that could degrade biodiversity and ecosystem services, is a financial measure to pay for Nature.

Non Financial

But it is important also to establish a mechanism to implement ecosystems, like policy laws, property rights and integrate decisions, in order to develop and use environmentally friendly technologies.


  1. Why has the economic valuation of nature not entered the mainstream of out society?

Nature and Environment are used in different ways, especially in tourism and tourism activities. A crucial question is:” it is possible to assign an economic value to nature and the environment?”. If this is possible to do, the decision-making process regarding the use of nature and the environment in tourism activities can be based on sound economic information. This facilitates the decision making process regarding the use of nature.

An important topic is the distinction between nature and the environment. In everyday language, they have approximately the same meaning and are used interchangeable.

In most cases, the environment is defined as the abiotic part of the ecosystem, which implies that water, air and soil pollution are the main issues involved. An additional issue is the use of natural resources such as iron, natural gas, wood and plastics. The latter are economic goods which normally have a price, as they are exchanged in a market. Water, air and soil pollution do not have a price, however. But with regard to water, air and soil pollution people are often economically affected. These costs for consumers and producers can be measured.

Nature, being the biotic part of the ecosystem, particularly in tourism, is not traded in a market which means that it is not possible to assign a suitable price to represent the economic value of nature. Beautiful beaches, mountain scenery and attractive Mediterranean landscapes, for example, are very important for tourists. They can be seen as an input in the production process of the tourism industry and have a high economic value. However, it is not clear how to measure these economic values.



  1. Do you think IAS is a serious concern in your region? Why or why not?

Surely IAS is a serous concern in my region, first because my region is an Island and second because Sardinia is in the middle of Mediterranean Sea, and not only a well known turistic area, but also an important trade spot because of its geographical position ( there are lot of ships movements either for oil and goods ). All those considerations are linked with questions and answers 1, 2 and 4.


10. Do you believe that humankind would protect biodiversity better if there were economic values assigned to ecosystem services? Why or why not?

Yes, I do.

First of all we have to increase awareness in biodiversity and also have to know all the consequences regarding our environmental management.

I was thinking about the economic value of great landscapes, well last year in a beautiful turistic place near the South East of Sardinia it occurred a huge oil spill, it was just inside a protected marine area and it was in may, incoming summer. Several mayors tried to figured out causes and management of that environmental but anthropogenic problem. Lots of experts in many topics gave their opinions, but really, in therms of technology or remote monitoring, nothing was done at regional level. As you can image that summer was affected by an economical loss, not only for the turistic reason, but also for the great efforts done by scientists to rescue marine and volatile species.

This is only one example, but it stress out that we have to give an economic value to Nature and Environmental as well, sometimes it will be difficult to do, but we have to try a kind of environmental market, like the carbon market established under the Kyoto Protocol, it could be assigned a certificate with some economic value to any of one ecosystem service at different national level.

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1) What is GMO?

A genetically modified organism (GMO) or genetically engineered organism (GEO) is an organism whose genetic material has been altered using genetic engineering techniques. These techniques, generally known as recombinant DNA technology, use DNA molecules from different sources, which are combined into one molecule to create a new set of genes. This DNA is then transferred into an organism, giving it modified or novel genes. Transgenic organisms, a subset of GMOs, are organisms which have inserted DNA that originated in a different species.

Genetic modification involves the insertion or deletion of genes. When genes are inserted, they usually come from a different species, which is a form of horizontal gene transfer. In nature this can occur when exogenous DNA penetrates the cell membrane for any reason. To do this artificially may require attaching the genes to a virus or just physically inserting the extra DNA into the nucleus of the intended host with a very small syringe, or with very small particles fired from a gene gun.

The use of GMOs has sparked significant controversy in many areas. Some groups or individuals see the generation and use of GMO as intolerable meddling with biological states or processes that have naturally evolved over long periods of time, while others are concerned about the limitations of modern science to fully comprehend all of the potential negative ramifications of genetic manipulation.

Some groups believe that underdeveloped nations will not reap the benefits of biotechnology because they do not have easy access to these developments, cannot afford modern agricultural equipment, and certain aspects of the system revolving around intellectual property rights are unfair to undeveloped countries.

The International Treaty on Plant Genetic Resources for Food and Agriculture has attempted to remedy this problem, but results have been inconsistent. As a result, "orphan crops" and indigenous plants, are important in the countries where they are grown, but receive little investment.

Another important controversy is the possibility of unforeseen local and global effects as a result of transgenic organisms proliferating.

An often cited controversy is a "Technology Protection" technology dubbed 'Terminator'. This technology would allow the production of first generation crops that would not generate seeds in the second generation because the plants yield sterile seeds. This technology is intended both to limit the spread of genetically engineered plants, and to require farmers to pay yearly to reactivate the genetically engineered traits of their crops.

In addition to the commercial protection of proprietary technology in self-pollinating crops such as soybean, another purpose of the terminator gene is to prevent the escape of genetically modified traits from cross-pollinating crops into wild-type species by sterilizing any resultant hybrids. The terminator gene technology created a backlash amongst those who felt the technology would prevent re-use of seed by farmers growing such terminator varieties in the developing world and was ostensibly a means to exercise patent claims. Use of the terminator technology would also prevent "volunteers", or crops that grow from unharvested seed.


2) What is genetic engineering in vitro?

Genetic engineering is a laboratory technique used by scientists to change the DNA of living organisms.

The term "genetic engineering" was coined in Jack Williamson's science fiction novel Dragon's Island, published in 1951 two years before Watson and Crick showed that DNA could be the medium of transmission of genetic information.

In vitro means literally "in glass " (from Latin: vitrum=glass). In in vitro experiments, organisms and structures are investigated under experimental conditions rather than in their natural context.

Genetic engineering, recombinant DNA technology, genetic modification/manipulation (GM) and gene splicing are terms that apply to the direct manipulation of an organism's gene. Genetic engineering is different from traditional breeding, where the organism's genes are manipulated indirectly infact GE uses the techniques of molecular cloning and transformation to alter the structure and characteristics of genes directly. Those techniques have found some successes in numerous applications. Some examples are in improving crop technology, the manufacture of synthetic human insulin through the use of modified bacteria and so on.

Molecular biologists have discovered many enzymes which change the structure of DNA in living organisms. Some of these enzymes can cut and join strands of DNA. Using such enzymes, scientists learned to cut specific genes from DNA and to build customized DNA using these genes. They also learned about vectors, strands of DNA such as viruses, which can infect a cell and insert themselves into its DNA.

With this knowledge, scientists started to build vectors which incorporated genes of their choosing and used the new vectors to insert these genes into the DNA of living organisms. Genetic engineers believe they can improve the foods we eat by doing this.

At first glance GE in vitro might look exciting to some people but deeper consideration reveals that could be either health and environmental hazard using indiscriminately this technology.



3) What kinds of GMOs are used now and will be used in future?

GMOs have widespread applications. They are used in biological and medical research, production of pharmaceutical drugs, experimental medicine, and agriculture.

Bacteria were the first organisms to be modified in the laboratory, due to their simple genetics. These organisms are now used for several purposes, and are particularly important in producing large amounts of pure human proteins for use in medicine.

Genetically modified bacteria are used to produce the protein insulin to treat diabetes or are also used in some soils to facilitate crop growth, and can also produce chemicals which are toxic to crop pests.

Transgenic Plants are mainly used nowadays in several countries, and are part of "The Global Diffusion of Plant Biotechnology: the global commercial value of biotech crops grown in the 2003–2004 was about US$44 billion.

Transgenic animals are also becoming useful commercially. On 6 February 2009 the US Food and Drug Administration approved the first human biological drug produced from such an animal, a goat.

In biological research, transgenic fruit flies (Drosophila melanogaster) are model organisms used to study the effects of genetic changes on development. Fruit flies are often preferred over other animals due to their short life cycle, low maintenance requirements, and relatively simple genome compared to many vertebrates.

Transgenic mice are often used to study cellular and tissue-specific responses to disease. This is possible since mice can be created with the same mutations that occur in human genetic disorders the production of the human disease in these mice then allows treatments to be tested.

Transgenesis in fish have been created for use in the aquaculture industry to increase the speed of development and potentially, reduce fishing pressure on wild stocks. None of these GM fish have yet appeared on the market, mainly due to the concern, expressed among the public, of the fish's potential negative effect on the ecosystem if they escape from fish farms.

Gene Therapy uses genetically modified viruses to deliver genes that can cure disease into human cells. Although gene therapy is still relatively new, it has had some successes. It has been used to treat genetic disorders such several immunodeficiency and treatments are being developed for a range of other currently incurable diseases.

I really can't assume that GMOs are good or not, but I think that the main concern is to study what is good for human and nature and what is wrong, and why. I think that GMOs future will be in developing and using carefully the genetic engineering, having always clear what we know and what we have to know about all the GMOs effect. Regarding this are good the risk assessment processes stressed about GMO and their products. All the risks for human and environment have to be regulated and studied (as well as for medicines or other goods that affected life).


4) GMO's products and natural products made by GMOs (examples)

The well known Big Four of GM Crops are Soybean, Maize, Rapeseed and Cotton.

Over half of the world's 2007 soybean crop (59%) was genetically modified, a higher percentage than for any other crop. Each year, the EU Member States import approximately 40 million tonnes of soy material, primarily used for feeding cattle, swine, and chickens. Soybeans are also used to produce many food additives.

Maize is the only GM crop that is currently being grown in Europe. Maize is used primarily for animal feed and is also an important raw material for the starch industry. If GM maize production in Europe were to increase, it would most likely make its way into food products.

Until recently, rapeseed was a relatively unimportant crop. Today rapeseed is grown not only as raw material for renewable resources, but also as a source of oil that is used to produce margarine. There is no GM rapeseed currently being grown in Europe. In Canada, however, GM rapeseed has become widespread.

Cotton is not only important as a source of fibre for textiles. The seeds make up an important part of food and animal feed. GM cotton is grown primarily in India, China and the United States. China is currently expanding its production of GM cotton, which could allow for drastic reductions in pesticide use.

No genetically modified fruit or vegetables are on the market in the EU. Any GM plants authorised in the EU are not intended for direct consumption.

Nevertheless, genetic engineering has become standard practice when it comes to research and crop improvement.

Ongoing projects are working on giving plants resistance to problematic pests and diseases.

For the most part, foods in European supermarkets are not genetically modified. But that doesn't mean genetic engineering doesn't play a role in the production of the food we eat each day.

Common ingredients that could be produced with genetic engineering are a) baked goods made of flour of GM soybean or olis from GM soybean or GM rapeseed; b) sweets products made of lechitin derived by GM soy, glucose or glucose syrup from GM maize, sugar from GM sugar beets, other additives, vitamines or enzymes from other GMOs.


5) What is risk assessment for GMOs?

The safety of GMOs in the foodchain has been questioned, with concerns such as the possibilities that GMOs could introduce new allergens into foods, or contribute to the spread of antibiotic resistance. Although scientists have assured consumers of the safety of these types of crops, consumption has been discouraged in many countries by food and environmental activist groups who protest GM crops, claiming they are unnatural and therefore unsafe. This has led to the adoption of laws and regulations that require safety testing of any new organism produced for human consumption. For that reasons the risk assessment considers the exposure of humans or the environment to genetically modified organism during the operation of, or possible unintended release from, a contained use facility.

Commission of the European Communities Guidance assumes the importance of risk assessment and outlined in council directive 90/219/EEC the use of genetically modified micro-organisms.

The risk assessment must take in consideration potentially harmful effects to human health and the environment.

Potentially harmful effects are defined as those effects which may give rise to disease, render prophylaxis or treatment ineffective, promote establishment and/or dissemination in the environment which gives rise to harmful effects on organisms or natural populations present or harmful effects arising from gene transfer to other organisms. The degree of risk arising from contained uses with a genetically modified organism, and their construction, is determined by consideration of the severity of the potential harmful effects, to human health or the environment, with the possibility of those effects occurring.

The full risk assessment process consists of two procedures outlined below:

Procedure 1

  • Identify potential harmful properties (hazard) of the GMO and allocate the GMO to an initial class taking into account the severity of the potential harmful effects.

  • Assessment of possibility of harmful effects occurring by consideration of exposure (both human and environmental) taking into account the nature and scale of the work, with containment measures appropriate to the initial class allocated.

Procedure 2

  • Determination of final classification and containment measures required for the activity.

  • Confirm final classification and containment measures are adequate by revisiting Procedure 1.

Aspects that should be considered are:

  • how relevant is the recipient organism;

  • the donor organism;

  • the insert;

  • the vector;

  • the resulting GMO;

  • last but not least human health and environmental considerations.

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1. Water Resources Management is not made by water managers alone. Identify the actors involved in the process and explain why they influence final management decisions?

Water is one of our most critical resources, but around the world it is under threat. This cross-cutting issue demands a coordinated approach. The success in avoiding a global water crisis is directly linked to the ability to address other global challenges from poverty eradication and environmental sustainability to fluctuating food and energy costs and financial turmoil in world economies. It is therefore imperative that global risks, including those associated with water, be dealt with in an integrated manner. We must develop interdisciplinary tools that can take into account different drivers such as climate change and financial markets to achieve sustainable water management. This requires the engagement of all stakeholders, particularly government leaders, as well as global coordination through the UN system.

Infact, in order to achieve a good governance of water resources, that is Integrated Water Resources Management, we can identify different dimension of actors: Social, Economic, Environmental and Political. So it is clear that all the actors are involved in the final management decisions.


2. Identify the type of drivers affecting water systems.

Important decisions affecting water management are made outside the water sector and are driven by external, largely unpredictable drivers – demography, climate change, the global economy, changing societal values and norms, technological innovation, laws and customs, and financial markets. Many of these external drivers are dynamic and changing at a faster place. Developments outside the water domain influence water management strategies and policies. Decisions in other sectors and those related to development, growth and livelihoods need to incorporate water as an integral component, including responses to climate change, food and energy challenges and disaster management. The analysis of these issues leads to a set of responses and recommendations for action that incorporate the contribution of water to sustainable development.



3. Identify the recent challenges of financing water systems.

So it is clear, the ‘water box’ dilemma must be resolved. Leaders in the water sector, water supply and sanitation, hydro-power, irrigation and food control have long been aware that water is essential to sustainable development, but they do not make the decisions on development objectives and the allocation of human and financial resources to meet them. These decisions are made or influenced by leaders in government, the private sector and civil society, who must learn to recognize water’s role in obtaining their objectives. These challenges cannot be separated from the challenges of sustainable development in a complex global context. So there is evidence of the need for public, private sector, civil society and communities to invest and become involved in water resources infrastructure and implementation capacity for the global environmental sustainability.

Bilateral donors, important in funding water investments, must avoid the temptation to reduce their aid budgets during the current global financial and economic crises. Like other physical infrastructure, water infrastructure deteriorates over time and needs repair and replacement. Investment is also required in operation and maintenance and in developing the capacity of the sector so that infrastructure meets appropriate standards and functions efficiently.



4. Discuss the cause-effect chains and links between water and MDG (Millennium Development Goals).

Water is essential for achieving sustainable development and the Millennium Development Goals. Actually, properly managing water resources is an essential component of growth, social and economic development, poverty reduction, equity and access to safe drinking water and adequate sanitation – all essential for achieving the Millennium Development Goals.

But, although those components are well established, they are also largely ignored.

It is not enough to hope that the trickle-down effects of economic growth will result in equitable distribution that includes the poor. The economic growth and poverty-reducing contributions of water resources must be made explicit and specific at the country level. Intergovernmental efforts must support such actions and maintain the momentum of the global commitments made since the Millennium Declaration in 2000. While mitigation of anthropogenic climate change is vital, the blunt reality is that all countries – particularly developing countries that will be hit hardest and earliest – and business sectors must also adapt to climate change. Even if greenhouse gas concentrations stabilize in the coming years, some impacts from climate change are unavoidable.

These include increasing water stress in many regions, more extreme weather events, the potential for large population migration and the disruption of international markets.


5. How participatory approach is important and can improve water management?

Water is a finite and vulnerable resource that must be sustained for future generations. Water is required to sustain the environment and support economic development as well. It is not only a gift of nature; it is part of human civilization shaping it in a variety of ways. It has a social and cultural value for human community. Today, when scarcity has turned water into an economic good, it has become a subject of political contention involving community rights, social rights with corporate demands posing a challenge for the State to evolve new policies. The goal of balancing the short-term and longer-term needs of society can best be accomplished through a participatory, democratic and pro-people management approach to environment that integrates land and water use across whole catchment areas and aquifers.

There are different approaches to water management such as institutional approach towards water management, scientific management for economic development, user management approaches to water management, private participation in water management and regulations, etc. For the purpose of overall development, resource management approach to water alone is not of much help instead an interdisciplinary perspective with participatory approach is what is required.

Specialists and managers in water supply and sanitation, hydro-power, irrigation and food control have long been aware of this. But they often have a narrow, sectoral perspective that blinds many decisions on water. And they do not make the decisions on development objectives and financial resources needed to meet these broader objectives. A coordinated action is required now. Lives and livelihoods depend on water for development. After decades of inaction, the problems are enormous. And they will worsen if left unattended. But while the challenges are substantial, they are not insurmountable. Recognizing the links between water resources and other crises around the world and between water resources and development, leaders in the water domain and decision-makers outside it must act together now to meet all the challenges on water resources management and sustainable development.


The World Water Assessment Program and its partners are working to help reduce uncertainty, facilitate decision-making and accelerate investment by highlighting the links between socioeconomic development and investment in water management capacity and infrastructure in other sectors. The challenges are great, but unsustainable management and inequitable access to water resources cannot continue. Actions must include increased investment in water infrastructure and capacity development. Leaders in the water domain can inform the processes outside their domain and manage water resources to achieve agreed socioeconomic objectives and environmental integrity. But leaders in government, the private sector and civil society will determine the direction that actions take.

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1. “Air quality models have several sources of uncertainties, but emission data are one of the most important and relevant sources.” Please comment this sentence, giving examples of other uncertainties sources and suggesting measures to reduce this uncertainty level.


Current air quality models generate deterministic forecasts by assuming perfect model, perfectly known parameters, and exact input data. This traditional approach, which is based on the use of one selected model and one data set of discrete input values, does not reflect the uncertainties due to errors in model formulation and input data mainly because our knowledge of the physics is imperfect! So we have to know how many uncertainties and how heavy they could be in a model in order to balance and to obtain the closer estimation of reality.

Uncertainties could be in emissions, chemical parameters, meteorological conditions, stochastic atmospheric processes, due to errors in some of the input parameters ( dimensions of the street, traffic volumes ) and also from exposure of humanity.

Given the complexities of different environments and the inherent limitations of mathematical modeling, it is unlikely that a single model based on routinely available meteorological and emission data will give satisfactory short-term predictions.

Finally, yes, it is globally assumed that emission data are one of the most important and relevant sources of uncertainties, and a probabilistic methodology for assessing air quality could reduce uncertainties (for example it is used the estimation of emission data by the product of activity data and emission factors).



2. Imagine that you are responsible for assessing the air quality over Sardinia region. Describe which kind of air quality models (global, regional/mesoscale and local scale) should you use and which input data would you need for it.


I will fragment the entire region in different local scale to forecast air quality in those local areas, seven at least, because of their different wind exposure, industrializations, land use and inhabitants distribution.

About input data:

- yet the division in seven local area of different kind of topography is an input data.

- meteorological data, which are necessary to assess the flows related to the processes of dispersion, mixing, deposition, chemical reactions, etc. It is therefore necessary to enter meteorological data as input for the area to be modeled and the period we wish to simulate.

- emission data, in Sardinia we have 50 monitoring stations spread all over the seven local area chosen before, that could measure different pollutants: BTX; CO; VOC; H2S; NOx; O3; PM<10 ìm; SO2 and TSP. Every industry is obliged to give emissions values that are validated by the measurements on the field. Thus we have to estimate different human exposure for any one of the pollutants.

The output of the air quality model, at local scale and with both meteorological and chemistry data will be a three dimensional distribution of pollutants concentrations.




3. Supposing that you were successful with the air quality simulation over Sardinia, which kind of air pollutants are you expecting to found with higher concentrations over the specific region of Cagliari? Justify.


Cagliari is the most populated area in Sardinia and also have different land use zones. Macchiareddu is an industrial area close to the city where it is also located a huge waste disposal, in Sarroch is located the oil industry Saras, Portoscuso is another industrial area in the ex-geominig zone of Sardinia, Campidano is the biggest agriculture area of the Region and goes from Cagliari City to Oristano City, but there are also many little enterprises that transform their foods product directly and in different ways.

So, the output of my air quality model will give me a three dimensional distribution of the concentrations of air pollutants over different area in the region.

I guess that over those different areas it would be great concentrations of :

  • In Macchiareddu, CO, SOx, NOx, PM10 and O3;

  • In Sarroch area the same pollutants above plus C6H6 and H2S;

  • In Portoscuso SO x, NO x and PM10;

  • In the Campidano area, SO x, NO x, H2S, PM10, O3




4. The “Po Valley” region is one of the most critical areas in terms of ozone in Europe. How can you justify that and describe the origin of these high levels of ozone?


The Po-valley located in northern Italy at the footstep of the Alps is characterized by a high density of anthropogenic emissions and by the frequent occurrence of stagnant meteorological conditions. The area has been identified as one hot spot place where pollution levels, not only O3 will remain problematic in spite of the application of the current European legislation devoted to air pollution control. By 2020, health impact on population and effects on ecosystems by ozone and eutrophication are indeed calculated to be amongst the highest in Europe and anthropogenic fine particulate matter levels are expected to be responsible for a loss of ten months of life expectancy.

Ozone in Po Valley is the photooxidation product made by NO x and VOC.

The rural soil is the main source of nitrogen oxides at this place.

The urban site exhibited a strongly VOC sensitive O3 production rate.

In many cases both VOC and NO x sensitive conditions were observed at the rural site.

The high-pressure conditions and the weak synoptic circulation favor the formation of strongly enhanced photooxidants and aerosol levels.

The polluted air masses are transported northward where the highest ozone concentrations of up to 200 ppb are reached 30 to 40 km away from the city center of Milan.



5. Explain the importance of an air quality forecasting system operational for a specific area or country.


Human exposure to some high concentrations of pollutants could affect deeply health and produce breath desease as well as could affect environment and nature.

There is an italian law derived by european law on air pollutants concentration values, Decreto Ministeriale n.60 of 02 april 2002. The law stress the importance of different limit values for each pollutant.

So not only one region should have that kind of air quality forecasting system, but also nations should have one, as a good starting point to evaluate environmental conditions and policy law planning to prevent and monitoring different pollutants concentrations. The goal is to give to public opinion and people real information on human and environmental safety linked to concentration levels of pollutants.

I underline that this kind of forecast is needed also for soil and water to obtain an entire overview of the problem.



Seminar “Human exposure to air pollution and smoke from forest fires”


1. Distinguish the main differences between the concepts of “concentration”; “exposure” and “dose” regarding the air pollution issue.


Reporting the scheme of a baseline of an air quality model:

sources > emissions > concentrations > exposure > dose > health effects,

it is clear that those three underlined concepts have different but important weight in air quality models.

Concentration: is a quantitative expression of the amount of pollutant within a given environmental medium. High air pollution concentrations do not necessary result in high exposures. For example, while air pollution concentrations may be very near an emitting industrial facility, high exposure will occur only if people spend time near the facility.

Exposure: can be defined as the event when a person comes into contact with a pollutant of certain concentration during a certain period of time. The concept of exposure is important both from the point of view of assessing the impact of a pollutant on health and from that of risk management, which often focuses on reducing people's exposure. Exposure to air pollution is largely determined by concentration of air pollutants in the environments where people spend their time, and the amount of time spend within them, either indoor and outdoor.

Dose: is a quantity expression which refers to the amount of pollution that actually crosses one of the body boundaries. So it is different from exposure and will be defined by the characteristics of exposure as well as a wide range of factors specific to the pollutant and by physiological factors such as person's level of activity, skin, condition and so on.



2. In the presented methodology to estimate human exposure over continental Portugal, what were the main week points of this approach?


To estimate human exposure you presented an exposure model mainly focused on air quality model and the concept of micro-environment.

For one individual exposure is given by the sum of concentration of a pollutant in one micro-environment plus time spent into the micro-environment, the total population exposure is the sum of all those individuals.

The perfection would be achieved if you know for every person the individual exposure, but this is impossible and you use statistical data. So you need to estimate, this is a weak point; infact you have to assume what are those different micro-environments and how many time the population spent into them, you have to divide population in urban and rural center or other and all those estimations would be logical in order to reduce the weak points of the assumptions.


3. There is a common methodology used to estimate emissions from forest fires. Which are the parameters/variables required to this estimation procedure?


Forest fires are a big concern of Mediterranean Countries. They affect biodiversity and environment, but also visibily, concentration of pollutants and particle matters and also human health.

The main pollutants emitted during a forest fire are: Ash, CO, VOC, PM10, NO x, CO2, CH4 and NO2.

The methodology used to estimate emissions from forest fire is a products of different terms.

Ei = EFi * b * B * A

where Ei is the emission of the forest fire; Efi is the emission factor and contains time; b is the burning efficiency and depends also on what kind of forest is burning and on meteorological conditions; B is the fuel load and A is the area burned.



4. What are the main important aspects that should be considered/involved in a forest fires modeling?


The main important aspect that should be considered in forest fire modeling is the fire progression model and other aspects such as the fire rates spread, the fire shape and growth, the fire index, weather and wind field simulation. Then the smoke dispersion system will give emissions direction.



5. “Firefighters are particularly affected by forest fire emissions”. Please comment this sentence and suggest possible measures that can be adopt in order to reduce these exposure values.


Firefighters often work under hazardous situations involving extreme fire behavior, topography and power tools and potentially health-compromising situations are commonplace. Because of the physical injuries such as cuts, burns and broken bones, the potentially debilitating effects of smoke inhalation are often viewed as just a job inconvenience.

Studies show that exposure to the chemical components of smoke can lead to negative health effects and other symptoms which may compromise worker performance. Most health problems are not long term, and can be managed using proper preventative techniques such as crew rotation through heavy smoke conditions and proper personal protective equipment.

Taking into account the monitoring campaign in summer 2008 in Portugal, presented during the seminar, it is clear that firefighters exhaled, after a fire job, different concentrations of pollutants than from normal people. Mainly a great concentration of CO, but also NO and other effect such a reduction of the volume of exhaled air during the first second (because of the PM10 inhaled) and an exhaled debit.

Management practices can protect firefighters from unnecessary exposure to smoke. Crews should be rotated through areas of heavy smoke and allowed to rest and recover in a smoke-free environment after every 7 to 9 days on the fireline.

These techniques can include using flank rather than head attack on fires where appropriate, minimizing mop-up activities and relying on burn-up rather than water to extinguish fires, avoiding inversion conditions, watering heliports and road to control dust, locating camps, staging areas, helibases and command posts in low smoke areas, using equipment rather than people in holding areas, designing burn plans with maximum allowable perimeters and more complete combustion, as well as providing masks and goggles as personal protection from the effects of smoke.

Firefighters can also be equipped with personal dosimeters to detect levels of carbon monoxide in the air and alarm in dangerous conditions and personal respirators and filtering masks. Providing effective protection is a difficult task, as firefighters are exposed to both toxic gases and dangerous particulates, and few technologies can protect against both. Firefighters have been known to use bandanas for protection in smoky areas, but they cannot defend against noxious gases. Bandanas do not create a seal between face and mask, protection is minimal and the material is often not fire resistant.

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  1. What does BAT mean in few words?

The concept of Best Available Techniques (BAT) was introduced as a key principle in the IPPC ( European Integrated Pollution Prevention and Control ) Directive 96/61/EC.

BAT is defined as the “most effective and advance stage in the development of an activity and its methods of operation, which indicate the practical suitability of particular techniques for providing, in principle, the basis for emission limit values designed to prevent or eliminate or, where that is not practicable, generally to reduce an emission and its impact on the environment as a whole”, where:

B: ‘best’ in relation to techniques, means the most effective in achieving a high general level of protection of the environment as a whole;

A: ‘available techniques’ means those techniques developed on a scale which allows implementation in the relevant class of activity under economically the technically viable conditions, taking into consideration the costs and advantages, whether or not the techniques are used or produced within the State, as long as they are reasonably accessible to the person carrying out the activity;

T: ‘techniques’ includes both the technology used and the way in which the installation is designed, built , managed, maintained, operated and decommissioned.


  1. What does BREFs mean? Report some examples.

The IPPC Bureau was set up to organise an exchange of information between Member States and industry on Best Available Techniques (BAT), associated monitoring and developments in them.

The European IPPC Bureau is an output oriented team which produces reference documents on Best Available Techniques, called BREFs. BREFs are the main reference documents used by competent authorities in Member States when issuing operating permits for the installations that represent a significant pollution potential in Europe. There are about 50000 of these installations in Europe.

In the international context, the European information exchange on best available techniques is considered to be an EU contribution to the global process initiated in 2002 at the World Summit on Sustainable Development so that non-EU countries can also reap the benefits of this ambitious work.


Some examples of Bref are: Waste Incineration Bref, Common waste Water and waste gas management System in chemical sector Bref, Industrial Cooling system Bref and other available on the link of European Commission joint Research centre EIPPCB

http://eippcb.jrc.es/reference/


  1. What is the purpose of soil remediation?

Generally, remediation means providing a remedy, so environmental remediation deals with the removal of pollution or contaminants from environmental media such as soil (also called Soil Washing or soil clean-up), water or other sediment, for the general protection of human health and the environment or from a brown-field site intended for re-development. Remediation is generally subject to an array of regulatory requirements, and also can be based on assessments of human health and ecological risks where no legislated standards exist or where standards are advisory.



  1. Which characteristics should be analyzed for design a soil washing plant?

First you have to know the physical and chemical characterization of dredged materials, second it is possible to point out the most suitable treatment among different processes and third it is possible to predict results and economical costs.

Soil washing is difficult when dealing with sediments because of the fine particles. The real problem is not the technique itself but the machineries used in the treatment.

The use of centrifuges and flotation columns can resolve the problem: actually those separators are able to separate particles of µm-dimension, that is the dimension characterizing the sediments.


  1. Please rank the following processes for cost of treatment:

Biological treatment – cheap, but you don't know how long it could be. Biological methods use micro-organisms for the degradation of the contaminants.

chemical/physics treatmenta good treatment, balance between cost/time/reuse of soil cleaned up. The purpose of the physical treatment is to concentrate the contaminants in a limited amount of sediment, generally by performing particle separation, basing on differences in grain size, specific gravity, magnetic susceptibility and surface properties.

thermal treatment expensive because of the elevated temperatures that are used in order to achieve physical and chemical processes.


  1. Indicate some solid –solid separation units for soil treatment.

The following soil – soil treatments were presented during the seminar:

Scrubber: it makes an attrition on contaminated sediment, leading to an extensive liberation of contaminants trough deglomeration and abrasion.

Magnetic separator: it exploits the differences in magnetic properties of particles.

Hydrofloat, flotation cell and column: they perform a wet separation based on differences in the surface properties of contaminant and non-contaminant particles.

Spiral: the principle is based upon the gradient which exists when particles of different densities are being transported by a water stream.


  1. Indicate some solid –liquid separation units for soil treatment.

Here following the solid – liquid treatments presented during the seminar:

Thickening: it is the dewatering step prior to filtration. It is more efficient when there is a large density difference between the liquid (generally water) and the solid particles.

Filtration: in the dewatering process thickening is followed by filtration. It is the process of separating solids from liquid by means of a porous medium which retains the solid but allows the liquid to pass.




 
 
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