Sweet and sour taste preferences of children
Liem, D.G. - \ 2004
Wageningen University. Promotor(en): Frans Kok, co-promotor(en): Kees de Graaf. - [S.I.] : S.n. - ISBN 9789085041054 - 200
consumptiepatronen - kinderen - voedselvoorkeuren - smaken - smaakgevoeligheid - zintuiglijke waarneming - zoetheid - zuurgraad - geur en smaak - consumption patterns - children - food preferences - tastes - taste sensitivity - organolepsis - sweetness - acidity - flavour
In the industrialized countries children have many foods to choose from, both healthy and unhealthy products, these choices mainly depend on children's taste preferences. The present thesis focused on preferences for sweet and sour taste of young children (4- to 12-years of age) living in the US and the Netherlands. Understanding how sweet and sour taste preferences are formed and modified can help health professionals and those working in industry, to develop strategies to decrease the consumption of sweet tasting foods and to increase the variety of children's diet with sour tasting foods. By using a variety of stimuli that differed in sweet (0.14M - 0.61M sucrose) and sour (0.00M - 0.25M citric acid) taste we investigated 1) how sweet and sour taste preferences of young children can be measured 2) which concentrations of sucrose and citric acid are most preferred 3) how repeated exposure modifies preferences and 4) how these preferences are related to oral physiological processes and food consumption. From the 7 studies we carried out it can be concluded that sweet and sour taste preferences of young children can consistently be measured with paired comparison and rank-order methods. Children prefer beverages with high concentrations of sucrose (0.61M) and a substantial part of children have a preference for extreme sour foods (0.08-0.25M citric acid). The later is related to intensity and novelty seeking behavior and consumption of fruits rather than oral physiological differences. Preferences for sour taste are related to exposure to sour taste during infancy and can not easily be changed by short repeated exposure during childhood. This is in contrast with preference for sweet taste, which can be heightened by a short repeated exposure during childhood. The knowledge gained by the present thesis may open the window to low-sweet and high-sour foods. This could be beneficial for fruit consumption and the dietary variety during childhood.
Verbeter Hibiscus met voeding
Aendekerk, T.G.L. - \ 2003
De Boomkwekerij 16 (2003)9. - ISSN 0923-2443 - p. 15 - 15.
houtachtige planten als sierplanten - hibiscus - plantenvoeding - fertigatie - zuurgraad - voedingsoplossingen - mestbehoeftebepaling - groeistoornis - misvormingen - ornamental woody plants - hibiscus - plant nutrition - fertigation - acidity - nutrient solutions - fertilizer requirement determination - failure to thrive - malformations
Onderzoek naar de invloed van pH en de voedingsoplossing op groeiafwijkingen bij Hibiscus. Gegevens in bijgaande tabellen: 1) Gebruikte voedingsoplossingen (waarden in mmol/l); 2) Beoordeling bij gebruikte voedingsoplossingen; 3) Optimale voedingsoplossingen (waarden in mmol/l) in twee periodes; 4) Optimale bemestingsniveaus in de potgrond (waarden in mmol/l).
Oorzaak vetsplitsing in melk niet altijd duidelijk
Slaghuis, B.A. - \ 2003
Praktijkkompas. Rundvee 17 (2003)2. - ISSN 1570-8586 - p. 14 - 15.
melken - machinaal melken - robots - automatisering - melkkwaliteit - melkveehouderij - melkvet - vetbolletjes - zuurgraad - landbouwkundig onderzoek - milking - machine milking - robots - automation - milk quality - dairy farming - milk fat - fat globules - acidity - agricultural research
Omdat de oorzaken niet duidelijk zijn, gaat het PV nader onderzoek uitvoeren naar vetsplitsing.
EU-project Automatisch Melken (3); melkkwaliteit & hygiene
Vorst, Y. van der; Koning, K. de - \ 2002
Praktijkkompas. Rundvee 16 (2002)3. - ISSN 1570-8586 - p. 18 - 19.
melken - machinaal melken - automatisering - robots - melkkwaliteit - melkveehouderij - melk - kwaliteit - melkhygiëne - kiemgetal - bacteriëntelling - zuurgraad - ph - melkvet - melkveebedrijven - onderzoeksprojecten - celgetal - milking - machine milking - automation - robots - milk quality - dairy farming - milk - quality - milk hygiene - bacterial count - bacterial counting - acidity - ph - milk fat - dairy farms - research projects - somatic cell count
Ditmaal is dat de melkkwaliteit. De kwaliteit is goed te noemen, maar de zuurtegraad van het melkvet is een punt van aandacht.
Overstroming en vegetatie: literatuurstudie over de effecten van overstroming op voedselrijkdom en zuurgraad
Sival, F.P. ; Jansen, P.C. ; Nijhof, B.S.J. ; Heidema, A.H. - \ 2002
Wageningen : Alterra (Alterra-rapport 335) - 66
vegetatie - inundatie - ph - redoxpotentiaal - voedingsstoffen - eutrofiëring - nederland - literatuuroverzichten - natuurontwikkeling - nutriënten - overstroming - laagveen - rivierkleigebied - voedselrijkdom - zuurgraad - vegetation - flooding - ph - redox potential - nutrients - eutrophication - netherlands - literature reviews
Door middel van een literatuurstudie aangevuld met kennis van water- en natuurterreinbeheerders betrokken bij lopende onderzoeksprojecten is getracht een beeld te vormen van de bestaande kennis en de kennishiaten. De effecten van inundatie op de redoxpotentiaal, zuurgraad, trofiegraad en de vegetatie worden beschreven. Ook is per fysisch-geografische eenheid (rivierklei-, laagveen en hogere zandgebieden) beschreven wat het effect is van inundatie.De uitkomsten van deze studie zijn ook gebruikt om kennishiaten te identificeren om zo richting te kunnen geven aan het vervolgonderzoek.
Stijging gehalte vrije vetzuren bij automatisch melken
Slaghuis, B. ; Koning, K. de - \ 2001
Rundvee praktijkonderzoek 14 (2001)1. - ISSN 1569-805X - p. 8 - 9.
melkmachines - machinaal melken - melken - melkinterval - robots - automatisering - melkkwaliteit - melkvet - zuurgraadwaarde - vetzuren - zuurgraad - melkveehouderij - milking machines - machine milking - milking - milking interval - robots - automation - milk quality - milk fat - acid degree value - fatty acids - acidity - dairy farming
Sinds de invoering van de melkrobot op bedrijven is te zien dat het gemiddelde gehalte aan vrije vetzuren omhoog gaat. Sommige bedrijven kampen zelfs met een korting voor vrije vetzuren.
|Validity of Ellenberg indicator values judged from physico-chemical field measurements
Wamelink, G.W.W. ; Joosten, V. ; Dobben, H.F. van; Berendse, F. - \ 2001
In: Vegetation and ecosystem functions; 44th IAVS symposium Freising-Weihenstephan. Freising (Germany), IAVS, 2001 - p. 189 - 189.
grondwaterstand - statistiek - vegetatie - zuurgraad
Historische pH en stikstofbeschikbaarheden in bossen en natuurterreinen
Kros, J. ; Mol-Dijkstra, J.P. - \ 2001
Wageningen : Alterra (Reeks Mileuplanbureau 14 / Alterra-rapport 217) - 27
stikstof - bodem - bodem ph - verzuring - zuurgraad - bossen - natuurreservaten - monitoring - modellen - nederland - nitrogen - soil - soil ph - acidification - acidity - forests - nature reserves - monitoring - models - netherlands
Op landelijke schaal zijn de zuurgraad en stikstofbeschikbaarheid in bossen en natuurterreinen berekend voor de jaren 1950 en 1980. Hiertoe zijn op landelijke schaal modelberekeningen uitgevoerd met het model SMART2 met gebruikmaking van historische depositiebeelden. De gemodelleerde pH-waarden zijn gevalideerd aan de hand van een beperkte set met historische metingen voor de jaren 1950, 1980 en 1990. De modelresultaten laten zien dat de pH tussen 1950 en 1980 gedaald is. Deze pH-daling is echter niet groot. Landelijk gemiddeld gaat het om een daling variërend van 0,2 pH-eenheden (laag 0-30 cm) tot 0,3 pH-eenheden (laag 0-60 cm). De gemodelleerde mediane stikstofbeschikbaarheid neemt in de periode 1950-1980 toe van 5 tot 7 kmol c per hectare per jaar.
The use of upscaling procedures in the application of soil acidification models at different spatial scales
Vries, W. de; Kros, J. ; Salm, C. van der; Groenenberg, J.E. ; Reinds, G.J. - \ 1998
Nutrient Cycling in Agroecosystems 50 (1998)1-3. - ISSN 1385-1314 - p. 223 - 236.
zure gronden - kattekleigronden - neerslag - chemische eigenschappen - zuurgraad - zure regen - modellen - onderzoek - geostatistiek - acid soils - acid sulfate soils - precipitation - chemical properties - acidity - acid rain - models - research - geostatistics
Different soil acidification models have been developed for use on different scales, i.e., NUCSAM for the local scale, RESAM for the regional (national) scale and SMART for the continental scale. This paper focuses on the uncertainties associated with scale transfer by a simpler model description by (i) temporal aggregation of process descriptions, (ii) neglection of processes associated with vertical aggregation of soil layers and (iii) the use of less detailed formulations of processes (process aggregation) and by spatial aggregation of input data. Results obtained for simulations in acid (sandy) soils indicate that (i) temporal aggregation and process aggregation have a limited impact on the long-term (decades) annual response of soil solution chemistry to atmospheric deposition, (ii) vertical aggregation mainly affects predictions of solutes which show a strong concentration gradient with depth and (iii) spatial aggregation hardly affects the average output for a given forest/soil combination. However, ignoring the variability in input parameters, largely affects the frequency distribution of model outputs in a region. Results imply that model simplification is an adequate step in the upscaling of modelling results from a local to a regional scale.
|Exposure of non-target plants to pesticides: a review on atmospheric concentrations and no-effect levels with special attention for herbicide vapours
Kempenaar, C. ; Tonneijk, A.E.G. ; Eerden, L.J. van der - \ 1998
Wageningen : AB-DLO - 20
gewasbescherming - pesticiden - herbiciden - lucht - hygiëne - luchtverontreiniging - neerslag - chemische eigenschappen - zuurgraad - zure regen - chemische samenstelling - planten - chemische analyse - plant protection - pesticides - herbicides - air - hygiene - air pollution - precipitation - chemical properties - acidity - acid rain - chemical composition - plants - chemical analysis
Effecten van hydrologische maatregelen tegen verzuring en vermesting op vegetatie, bodem en grondwater in Groot Zandbrink; evaluatie na vijf jaar
Jansen, P.C. ; Kemmers, R.H. ; Delft, S.P.J. van; Knol, W.C. - \ 1997
Wageningen : DLO-Staring Centrum - 64
ecologie - hydrologie - rivieren - waterlopen - kanalen - water - oppervlaktewater - waterverontreiniging - waterkwaliteit - neerslag - chemische eigenschappen - zuurgraad - zure regen - bodemchemie - anorganische verbindingen - mineralen - graslanden - nederland - ecohydrologie - gelderland - gelderse vallei - ecology - hydrology - rivers - streams - canals - water - surface water - water pollution - water quality - precipitation - chemical properties - acidity - acid rain - soil chemistry - inorganic compounds - minerals - grasslands - netherlands - ecohydrology - gelderland - gelderse vallei
In het natuurreservaat Groot Zandbrink zijn greppels aangelegd in natte schraalgraslanden als maatregel tegen verzuring. Sinds 1991 worden de ontwikkelingen in vegetatie, bodem en grondwater gevolgd. Daartoe wordt ieder jaar de vegetatie gekarteerd enwordt de bodem om de twee jaar en het bodemwater ieder kwartaal bemonsterd. Op verschillende plekken bleek de maatregel in natte perioden effectief: de calciumverzadiging en het aandeel lithotroof water in de wortelzone nam toe, terwijl ook de bedekking met kwelafhankelijke plantensoorten groter werd. Tijdens de droge periode juni '95-oktober '96 zijn de veranderingen echter teniet gegaan. Verder toonde het onderzoek aan dat in vergelijking met de periode 1978-1981 de hoogste grondwaterstanden minder langdurig bereikt worden en de gemiddeld laagste grondwaterstand is gedaald.
|Verzuring in Nederland; indirecte effecten
Erisman, J.W. ; Vries, W. de - \ 1997
Bodem 7 (1997)3. - ISSN 0925-1650 - p. 109 - 111.
bodem ph - bodemaciditeit - neerslag - chemische eigenschappen - zuurgraad - zure regen - nederland - soil ph - soil acidity - precipitation - chemical properties - acidity - acid rain - netherlands
Invloed van milieubedreigingen op de natuurwaarden van het Nederlandse bos. Basisdocument voor Natuurverkenning '97
Hendriks, C.M.A. ; Jansen, P.C. ; Schotman, A.G.M. ; Vries, F. de; Kemmers, R.H. ; Olsthoorn, A.F.M. ; Schaap, W. - \ 1997
Wageningen : SC-DLO (Rapport / DLO-Staring Centrum 413) - 104
bosbouw - achteruitgang, bossen - levensvatbaarheid - synecologie - milieu - verontreinigende stoffen - verontreiniging - nadelige gevolgen - verdroging - drogen - neerslag - chemische eigenschappen - zuurgraad - zure regen - forestry - forest decline - viability - synecology - environment - pollutants - pollution - adverse effects - desiccation - drying - precipitation - chemical properties - acidity - acid rain
Validation and application of soil acidification models at local, national and European scale; a compilation of articles on the models NuCSAM, ReSAM and SMART
Kros, J. ; Groenenberg, J.E. ; Salm, C. van der; Vries, W. de; Reinds, G.J. - \ 1996
Wageningen : DLO Winand Staring Centre - 158
zure gronden - kattekleigronden - bosbouw - neerslag - zure regen - zure depositie - chemische eigenschappen - zuurgraad - modellen - onderzoek - acid soils - acid sulfate soils - forestry - precipitation - acid rain - acid deposition - chemical properties - acidity - models - research
An overview is given of three dynamic soil acidification models for application on different spatial scales. NUCSAM, the model for the local scale, was validated on data from two intensively monitored research sites. Results of annual average soil solution concentrations and fluxes calculated with the validated NUCSAM model agreed well with those of the national-scale model RESAM and to a lesser extent with those of the European-scale model SMART. Various deposition scenarios for SOx, NOx and NHx on soils were evaluated with the three acidification models.
Invioed van de zuurtegraad van varkensurine op de ammoniakemissie
Eizing, A. ; Aarnink, A.J.A. - \ 1996
Wageningen : IMAG-DLO (Rapport / Dienst Landbouwkundig Onderzoek, Instituut voor Milieu- en Agritechniek 96-02) - ISBN 9789054061397 - 27
varkenshouderij - vleesproductie - vleesvee - urine - luchtverontreiniging - ammoniakemissie - vervluchtiging - guanine - hypoxanthinen - hippurinezuur - ph - zuurgraad - waterstofionen - mengmeststoffen - varkensmest - pig farming - meat production - beef cattle - urine - air pollution - ammonia emission - volatilization - guanine - hypoxanthines - hippuric acid - ph - acidity - hydrogen ions - compound fertilizers - pig manure
Dit rapport beschrijft het effect van een lagere urine-pH op de ammoniakemissie in een varkensstal. Het onderzoek is uitgevoerd in een modelopstelling met de zogenaamde stalsimulator, waarbij de invloed van de urine-pH op de ammoniakemissie werd onderzocht. Hiervoor werd de urine van vleesvarkens op balanskooien gescheiden van de faeces opgevangen. De pH werd gevarieerd door het toevoegen van fosforzuur of hippuurzuur aan de urine.
Long-term changes of chemistry and biota in moorland pools in relation to changes in atmospheric deposition
Dam, H. van; Houweling, H. ; Wortelboer, F.G. ; Erisman, J.W. ; Smeulders, S.M. - \ 1996
Wageningen : DLO Institute for Forestry and Nature Research (IBN Research Report 96/6) - 147
meren - reservoirs - plassen - water - waterverontreiniging - waterkwaliteit - eutrofiëring - chemische eigenschappen - neerslag - zuurgraad - zure regen - zwampen - moerassen - wetlands - lakes - reservoirs - ponds - water - water pollution - water quality - eutrophication - chemical properties - precipitation - acidity - acid rain - swamps - marshes - wetlands
An economic analysis of tradeable emission permits for sulphur dioxide emissions in Europe
Kruitwagen, S. - \ 1996
Agricultural University. Promotor(en): H. Folmer; L. Hordijk. - S.l. : Kruitwagen - ISBN 9789054855842 - 235
neerslag - chemische eigenschappen - zuurgraad - zure regen - atmosfeer - milieu - overheidsbeleid - milieubeleid - milieuwetgeving - luchtverontreiniging - bodemverontreiniging - waterverontreiniging - lucht - hygiëne - economisch beleid - instrumenten (meters) - vergunningen - zwaveldioxide - kwaliteit - conservering - landen van de europese unie - maatregelen - precipitation - chemical properties - acidity - acid rain - atmosphere - environment - government policy - environmental policy - environmental legislation - air pollution - soil pollution - water pollution - air - hygiene - economic policy - instruments - permits - sulfur dioxide - quality - conservation - european union countries - measures
This study has examined the question of whether a system of tradeable emission permits can contribute to a cost-effective reduction of SO 2 emissions in Europe, taking into account prespecified deposition targets and what sort of system it should be. To deal with this question three research topics have been examined.
(I) What are the main economic aspects of a European acid rain policy?
(II) What are the advantages and the disadvantages of using a system of tradeable permits to implement a European acid rain policy?
(III) What should a system of tradeable emission permits for a non-uniformly mixing pollutant look like in order to take deposition targets into account?
This chapter summarizes and presents the conclusions of this research. First 1 present the conclusion on the efficacy of the different integrated assessment models in analysing the effects of emission reduction. I then summarize the conclusions on guided bilateral permit trading. Finally, I make several suggestions for further research.
7.2 Economic theory of pollution control
Another issue I discussed is which policy instruments can be used to implement pollution control policy. A main distinction can be made between economic and non- economic instruments (regulation). A main advantage of economic instruments is their cost-effective character because, unlike regulation, economic instruments result in minimum control costs. Moreover, they allow more flexibility to the polluters and provide a continuous incentive for developing and adapting new control technologies. This thesis has elaborated on the use of tradeable emission permits.
7.3 Tradeable permits for non-uniformly mixing pollutants
It cannot be concluded in general that emission permits are a suitable instrument for controlling non-uniformly mixing pollutants. The use of emission permits results in a cost-minimum reduction of emissions, but the enviromnental implications of this emission reduction are uncertain, as deposition may be unacceptably large at some locations. To what extent the resulting cost-effective emission allocation deviates from the cost-effective deposition allocation depends on the source-receptor relationships and the marginal control costs of controlling the sources. In the USA, however, tradeable emission permits are actually used for the non-uniformly mixing pollutant SO 2 . Nevertheless, one should be aware that this emission trading does not focus on reaching a deposition target, but is only emission oriented. Environmental targets are taken care of by State Implementation Plans in the USA.
Deposition permits are an obvious alternative to emission permits for taking emission location into account. Theoretically, the use of tradeable deposition permits results in a cost-effective allocation that meets deposition targets. According to this system, sources have to own the appropriate number of deposition permits for each receptor affected. In this way authorities can control deposition targets. However, a disadvantage of this system is that it may result in an increase in emissions, which is politically delicate. Another argument against this system is the trading complexity that occurs because sources have to operate simultaneously in many different markets.
Since the use of both emission and deposition permits is not considered to be a very suitable instrument, several alternatives permit systems for non-uniformly mixing pollutants have been proposed in the literature. Relatively simple alternatives are permit trading within zones and the 'worst case' approach, but unfortunately, these systems do not guarantee the non-violation of deposition targets.
A promising permit trading system that does not violate deposition targets seems to be a more advanced one where the trading is subject to rules. Three variants are known: the pollution offset, the non-degradation offset and the modified pollution offset. All systems guarantee non-violation of deposition targets. The constraints on emissions and on deposition targets, however, differ between these systems. The pollution offset offers the largest trade opportunities, but allows for an increase in emissions. The non-degradation offset and the modified pollution offset are more restricting and consequently result in higher abatement costs. Which of the two has the lower cost cannot be shown on theoretical grounds.
In judging permit trading systems, special attention has to be paid to the nature of the trading process. Although many studies implicitly assume a simultaneous trading process, it seems more reasonable to consider permit trading as a bilateral and sequential process. Combining permit trading subject to rules with the bilateral and sequential trading concept sheds new light on the cost-effectiveness of these permit trading systems. Empirical studies indicate that bilateral permit trading applying offset rules do not result in cost-effective abatement. However, bilateral and sequential trading has only been recently applied to studies on permit trading, and has been examined further in this study. A main conclusion is that permit trading for non-uniformly mixing pollutants has to be restricted in some way if deposition targets are to be taken into account. What is needed are restrictions that result in non-violation of deposition targets, and at the same time, do not hamper the attainment of the cost-effective allocation.
7.4 Integrated assessment models
Among the European integrated assessment models, the RAINS model is the most complete and extensive. Although the RAINS model, the ASAM and the CASM are roughly similar, they diverge on various points as well. One difference is the number of acidifying compounds they take into account. Other differences are the optimization options that are implemented and the accuracy of the emission location. Finally, the data sources used differ in some submodels. The main benefit of the ASAM is its accuracy on emission locations and the resulting atmospheric transport. However, because of lack of data for this purpose, the intended accuracy is only partial. Model results show no significant differences caused by the grid to grid approach used. A serious drawback of this model is the lack of clarity of the procedure needed to derive the so called Best Economic Environmental Pathway. The CASM is attractive because of its large number of optimization criteria. However, since policy aims at reaching certain deposition targets, optimization criteria to minimize environmental damage, given a budget constraint are not actually very useful for policy purposes. Comparison of the CASM and the RAINS model shows that the model results are broadly in line with each other.
There are two reasons for the current status of acceptance of the RAINS model. First, the model is the most completely integrated assessment model for acidification. The alternative integrated assessment models, the CASM and the ASAM do not substantially improve the RAINS model. Second, RAINS was developed by scientists of various disciplines at an international "East-West" institute. This aspect mainly played a role in the acceptance of RAINS in international policy making (Hordijk, 1991, 1995). Acid rain models have substantially increased knowledge of the acid rain problem and have provided useful information for assisting and improving policy making. In this research I used the RAINS model for calculations. The reasons for this choice were those given above: (i) the model is the most complete one for acidification and (ii) the model is widely accepted and was used in the international negotiations on the Second Sulphur Protocol.
7.5 Guided bilateral trade
Guided bilateral permit trading achieves a cost-effective allocation if all trade transactions that are in accordance with the trade vector are profitable. A drawback of guided bilateral permit trading is that trade transactions are not necessarily profitable. Whether this is so depends on the source-receptor relationships, the abatement cost functions, the deposition targets and the initial permit distribution. To reach the deposition targets ultimately, non-profitable trade transactions need to be compensated in some way. Before trade transactions can be guided to the costeffective emission allocation, this allocation has to be known. Therefore full information is required by the trade institution in order to establish the trade vector. Unfortunately, this cancels out one of the characteristics of tradeable permits, namely that full information is not needed. Knowledge on the costeffective emission allocation by policy makers might cause the guided bilateral permit system to become unnecessary. However, knowing this allocation does not by definition imply that it will be agreed upon at once, as can be seen from the Second Sulphur Protocol. In that case, a suitable instrument for achieving further cost savings is a system of guided bilateral trade.
The term guided bilateral trade indicates that the permit market as such is not able to generate the desired outcome. The trade process has to be guided by a trade institution that takes care of the number of traded permits. However, any trading system that takes deposition targets into account will need some kind of control. The main advantage of the guided bilateral trade system is that the costeffective emission abatement allocation can be achieved if all trade transactions are profitable, or, if not, when non profitable transactions are subsidized. In the past, achieving the cost- effective allocation was thought to be possible by means of a simultaneous trade process. However, as I indicated in section 5.3, the practical functioning of such a trade system is a black box. This box can be opened by means of the system of guided bilateral trade.
To examine to what extent the guided bilateral trade system results in a costeffective reduction of S02 emissions in Europe, taking into account deposition targets, I used the RAINS model to simulate guided bilateral permit trading among European countries for SO 2 emissions. In calculating the cost-effective emission allocation, emission is measured at national level. Accordingly, guided bilateral permit trading only allocates emission reduction between countries. The way in which countries meet their emission reduction is a next step. For the sake of completeness it should be noted that the European abatement allocation is only cost-effective if all individual countries also reduce their national emissions in a cost minimum way. I simulated guided bilateral permit trading for three cases. In the policy oriented Base Case, permit trading aimed at the cost-effective emission allocation, given the Current Reduction Plans of the European countries. In variant 1 the restriction of Current Reduction Plans was released. Variant 2 examined guided bilateral permit trading, starting from the SO 2 Protocol.
The simulation results indicated that permit trading steers the trade process towards the cost-effective allocation of emission abatement, but the cost-effective allocation of emission abatement will not be fully reached by profitable trade transactions. In all three cases, the profit generated by guided bilateral permit trading was substantial. In the Base Case and in variant 1, the cost saying of permit trading amounted to 13.5% of the total abatement costs. From a policy point of view, variant 2 is very interesting since it draws heavily on the actual situation in Europe. The simulation result of Variant 2 indicated that guided bilateral permit trading, starting from the emission allocation in the Second SO 2 Protocol, results is a cost saving of 7.8% of the total abatement costs. Given this result, we may conclude that, compared to the SO 2 Protocol, some cost-effective improvement is possible by guided bilateral permit trading. However, it should be noted that the simulation results excluded transaction costs. Therefore, the indicated cost savings can be regarded as the upper limit of possible savings.
The simulation results indicated that the trade sequence influenced the generated profit. However, the simulations showed that the impact of trade sequences on the profit level was small. This suggests that a trade coordinating institute does not have to play an active role in the matching of trade partners, but only has to control whether countries trade according to the trade vector.
Having discussed the main aspects of this study I now want to turn to the third research question. By developing the guided bilateral permit trading system I have shown how a permit trading system for non-uniformly mixing pollutants could be formulated that takes deposition targets into account. The main drawback of this system is that full information on the cost-effective allocation is needed by the environmental authorities if such a trading system is to be successfully implemented. But, it should also be realized that in the current practice this information has already been used: in the negotiations on the Second Sulphur Protocol the information on the cost-effective emission allocation provided by the RAINS model served as a guideline for the agreed emissions reduction. Since countries agreed upon the emission reductions in the Second Sulphur Protocol, they might agree on a permit trading system that is based on the same information.
7.6 Guided bilateral trade revisited
The system of guided bilateral permit trading succeeds in reaching the cost-effective abatement allocation if all allowed trade transactions are profitable. If not, the cost- effective allocation will only be fully reached if the trade transactions needed to reach this cost-effective allocation are subsidized. This will be difficult since it is necessary to prune away profits from profitable trades to generate funds for subsidizing. However, the simulation results of guided bilateral permit trading indicate that the violation of deposition targets is only very moderate if the costeffective allocation is not fully reached by guided bilateral permit trading. Therefore it can be stated that guided bilateral permit trading is sufficient for the cost-effectiveness criterion. Arguments generally favouring the use of tradeable emission permits are that the use of permits provides a continuous incentive to search for technology innovation and provides flexibility to polluters in the way they want to comply with the environmental targets. Guided bilateral trade provides this incentive and flexibility as well.
An important aspect in judging the suitability of guided bilateral permit trading is the conformity with international agreements. In this thesis 1 have shown that given the Second Sulphur Protocol, guided bilateral permit trading can improve the cost- effectiveness of emission abatement. Whether a system of guided bilateral permit trading will really be successful will largely depend on the willingness of the European countries to accept the specified trade rules and the initial distribution of permits. A disadvantage for negotiating countries may be that emission permits, by definition, put a price on pollution that was previously free. To make permits acceptable, countries first have to receive permits for free. In this thesis it was suggested that the agreed emission levels from the Second Sulphur Protocol could serve as a guideline for the initial distribution of permits, since countries have already committed themselves to these amounts. In fact, given the current sulphur protocol, the guided bilateral permit trading system provides a 'recipe' for reaching the cost- effective sulphur dioxide allocation in Europe. Since the sulphur protocol is an agreement among national governments, permit trading among these governments is an obvious succession. However, alternatively, a system could be implemented in which permit trading could take place among firms (see section 7.7).
The costs of implementation of a guided bilateral permit trading system have not been studied in this research and it is therefore difficult to judge the system on this criterion. However, compared to the current international practice of negotiations, there seems to be no indication so far that the costs of this trading system will be substantially higher. Neither the distributional aspects of guided bilateral permit trading have been dealt with extensively. In general, no country will be worse off with permit trading, since a country will only trade permits if this results in a profit, resulting in a Pareto improvement. A country selling permits will only sell permits if the permit price exceeds the marginal abatement costs, and a country will only buy permits if this is cheaper than emission abatement. So, in so far as the abatement costs of countries change as a result of permit trading, this change is always compensated by the buying or selling of permits. Therefore, guided bilateral permit trading will only result in very moderate distributional effects.
The most obvious way for practical implementation of guided bilateral permit trading is to extend the Second Sulphur Protocol with a guided bilateral permit trading scheme in an additional annex, in accordance with annex II in which the current committed emission reductions are stated. Currently, countries are obliged to report the annual levels of sulphur emissions to the Executive Body of the Convention each year. Likewise, countries could be obliged to report their trade transactions annually. I suggest that it is better to include a trade scheme in the protocol rather than the trade vector, since a trade scheme as presented in Table 6.15 or 6.16 results in the largest cost savings. Furthermore, by presenting a trade scheme, countries do not have to search for their trading partner. This form of implementation does not require the establishment of a new agency since it fits into the current international negotiation arrangement on acidification, through the Convention under the Economic Commission for Europe of the United Nations.
In this section I have indicated that guided bilateral permit trading principally offers a suitable supplement to the sulphur protocol for reaching a cost-effective emission allocation. I have also indicated how such a trading system could be implemented. Remembering that the simulation results showed that guided bilateral permit trading may generate a cost saving of 143 million DM, this system can be taken as a suitable policy instrument for reducing sulphur dioxide emissions. Whether it can really be successfully implemented largely depends on the political willingness of countries to accept such a trading scheme.
7.7 Suggestions for further research
(i) In this study I have assumed permit trading takes place among national governments. One justification for this is that a permit trading system has a fair chance of being accepted if it is close to the current multiparty negotiations that assign targets to nations, as in the sulphur protocols. An alternative would be that emission permits be distributed to and traded by firms. Arguments in favour of this are that national governments lack experience and lack knowledge about operations and compliance options at the firm level. The question is what guided bilateral permit trading would look like if trading took place among firms. Although the general methodology of guided bilateral permit trading needs no modification, if trading is taking place among firms rather than among countries, its implementation requires additional research. To simulate permit trading among firms, additional data are needed. The source receptor matrix has to be adapted since it is the location of firms that matters now. The source receptor matrix has to link the firm's emissions to deposition, Moreover, abatement costs have to be specified at the firm level. The current RAINS-Europe model does not contain these necessary data and refinements. However, the RAINS-Asia model, a policyoriented model which provides a framework for integrated assessment of acid deposition in Asia, does already provide an analysis for large point sources. In this model, the emissions of 355 large point sources are linked to deposition at 1°x 1° grid cells (Foell et al., 1995).
Alternatively, permit trading between firms could be analysed by a 'two-stage method'. This method, which needs no modification of the source receptor matrix, consists of first selecting two trading countries and next of selecting the firms with the lowest and the highest marginal control costs within these countries. Obviously, the firm with the lowest marginal costs is selected for the country selling permits and the firm with the highest marginal costs for the country buying permits. The next trade would be between the firms with the second highest and the second lowest costs, and so on.
(ii) Acidification is not only caused by sulphur dioxide emission, but also by nitrogen oxides and ammonia. Instead of analysing trade in of sulphur permits, as I have done in this thesis, it would be interesting to study the opportunities for the use of tradeable permits for total acidification. This multipollutant approach is in accordance with the ongoing negotiations on a following protocol on acidification. However, it requires additional research, including the following topics. Firstly, the three pollutants contribute in a different way to acidity. This would lead to possible substitution of emission reduction. Further, spatial patterns of emission and deposition differ, and abatement-cost functions show differences. These differences imply that permit trading for total acidification will be complex, but considering all acidifying emissions simultaneously may provide additional cost savings. An interesting topic to analyse in this context is how to allocate the emission reductions of sulphur dioxide and nitrogen oxides as the latter contribute both to acidification and to tropospheric ozone. The role of nitrogen oxides in acidification has been discussed in Chapter 1. Tropospheric ozone is formed by complex chemical reactions of volatile hydrocarbons (VOC) and nitrogen oxides. The ratio of VOC and NO x , and not merely their total amounts, is important for ozone formation. This implies that when the ratio of VOC to NO x is very small, reduction of NO x , can actually increase ozone formation. In general, the abatement of nitrogen oxide is more expensive than the abatement of sulphur dioxide. This implies that a shift from nitrogen oxides to sulphur dioxide emission reduction would result in cost savings. However, as nitrogen oxides contribute to tropospheric ozone, preventing high ozone concentrations might, in some cases, prohibit the reduction of nitrogen oxides. An additional restriction on NO x emissions would be needed to take this into account in a permit trading system .
(iii) A third extension of guided bilateral permit trading for sulphur dioxide emission would be to link sulphur dioxide emission to climatic change. The rationale for this is that both problems have a common source, that is, energy use. In the RAINS model for Europe which was used for this study, only end-of-pipe technologies are available for reducing emissions. However, changes in energy use may be of benefit to both acidification and climatic change. To analyse the effect of changes in energy use for sulphur dioxide emissions the RAINS model should be extended with an accurate energy scenario module. The RAINS-Asia model is already equipped to generate energy scenarios. The so called energy scenario generator in this model estimates energy consumption contributing to SO 2 emissions (Foell et al., 1995).
(iv) A final topic for further research is how to implement a system of guided bilateral permit trading if a protocol had not yet been signed. Given an agreed initial permit allocation and given the restriction of the trade vector, it would be obvious to provide the opportunity to trade emission permits. Countries will have a strong incentive to trading since this is beneficial in terms of costs. If it appeared that countries would not trade, this could be an indication that transaction costs are too high. If transactions costs exceeded the indicated cost savings, permit trading would not take place, and countries would comply with the emission reduction without trading.
It has become clear that research on tradeable emission permits for sulphur dioxide emissions is an interesting topic that needs further investigation. Extending the research by the suggested options may provide new insights into how to achieve emission reductions at minimum abatement costs. Especially growing economies, such as those in Asia and Latin America, that will suffer from sulphur dioxide emissions and deposition in the near future, can benefit from a better insight into tradeable emission permits for reaching cost-effective reductions.
|Invloed van aanzuren op het gehalte aan vluchtige vetzuren in verse vleesvarkensmengmest = Effect of acidification on the concentration of volatile fatty acids in fresh pig slurry
Hoeksma, P. ; Vijn, T.K. ; Derikx, P.J.L. - \ 1995
Wageningen : IMAG-DLO (Rapport / Dienst Landbouwkundig Onderzoek, Instituut voor Milieu- en Agritechniek 95-16) - 30
mest - vloeibare meststoffen - rundveedrijfmest - luchtverontreiniging - ammoniak - emissie - vervluchtiging - ph - zuurgraad - waterstofionen - mestoverschotten - mestverwerking - manures - liquid manures - cattle slurry - air pollution - ammonia - emission - volatilization - ph - acidity - hydrogen ions - manure surpluses - manure treatment
Modelling of soil acidity and nitrogen availability in natural ecosystems in response to changes in acid deposition and hydrology
Kros, J. ; Reinds, G.J. ; Vries, W. de - \ 1995
Wageningen : SC-DLO (Report / DLO Winand Staring Centre 95) - 90
bodem ph - bodemaciditeit - bodem - stikstof - plantengemeenschappen - vegetatie - onderzoek - ecologie - hydrologie - neerslag - chemische eigenschappen - zuurgraad - zure regen - modellen - ecohydrologie - soil ph - soil acidity - soil - nitrogen - plant communities - vegetation - research - ecology - hydrology - precipitation - chemical properties - acidity - acid rain - models - ecohydrology
Changes in vegetation are often caused by changes in abiotic site factors. The SMART2 model has been developed to evaluate the effects of changes in ion inputs by atmospheric deposition and seepage on these site factors. Linkage with the Multiple Stress Model for Vegetation (MOVE) enables evaluation of the effects on the occurrence probability of vegetation species in response to deposition and seepage scenarios. Combinations of two deposition and two seepage scenarios were evaluated with SMART2. Results focused on pH, nitrogen availability and base saturation. Effects of changes in pH on the occurrence probability of forest understorey in a nutrient-poor deciduous forest were evaluated with MOVE.
|Scenario studies on soil acidification at different spatial scales
Vries, W. de; Kros, J. ; Groenenberg, J.E. ; Reinds, G.J. ; Salm, C. van der; Posch, M. - \ 1995
In: Scenario studies for the rural environment : selected and edited proceedings of the symposium scenario studies for the rural environment, Wageningen, The Netherlands, 12 - 15 September 1994 / Schoute, J.T.H., Finke, P.A., Veeneklaas, F.R., - p. 169 - 188.
zure gronden - kattekleigronden - neerslag - chemische eigenschappen - zuurgraad - zure regen - modellen - onderzoek - acid soils - acid sulfate soils - precipitation - chemical properties - acidity - acid rain - models - research
Three dynamic soil acidification models have been developed for application on local, national and continental (European) scales, namely NUCSAM, RESAM and SMART. This paper gives an overview of results of various model validation and scenario studies for the effects of SOx, NOx and NHx deposition on soils. Furthermore, the various strong and weak points of the models are evaluated in terms of uncertainties in model predictions, the use of the models in acidification abatement policies, and the limitations and possibilities of using the models in other scenario studies, such as changes in land use, hydrology and heavy-metal deposition.