Sustainable Fuel Practices in Roman North Africa and the Contemporary Mediterranean Basin

IF 0.2 Q4 ANTHROPOLOGY
Erica Rowan
{"title":"Sustainable Fuel Practices in Roman North Africa and the Contemporary Mediterranean Basin","authors":"Erica Rowan","doi":"10.24916/IANSA.2018.2.2","DOIUrl":null,"url":null,"abstract":"As a readily available and renewable resource, olive pomace has been used as a fuel throughout the Mediterranean for centuries. This article will first discuss the extensive use of pomace fuel in Roman North Africa, introducing and adding the once coastal city of Utica to our growing list of sites with archaeobotanical evidence for pomace residue. The paper will then focus on the ways in which the Romans linked olive oil and pottery production. While environmental sustainability was unlikely to have been one of the Romans’ conscious objectives, the use of this fuel was vital to the continued production of North African ceramics, particularly in more arid areas. Today, in the face of increasing energy demands, pomace is once again being recognized as an important and sustainable resource. More work, however, still needs to be done to improve the efficiency of pomace use. The article will conclude by highlighting the valuable lessons that can be learned from ancient practices, especially the efficient pairing of olive cultivation and pottery production. IANSA 2018 ● IX/2 ● 147–156 Erica Rowan: Sustainable Fuel Practices in Roman North Africa and the Contemporary Mediterranean Basin 148 pomace fuel assemblages from olives burnt for ritual purposes or as table waste. In all cases, the burning, or carbonization process, turns the olive flesh and skin to ash and as a result we are often only left with burnt olives stones (endocarps) and occasionally the seeds. Usually a pomace assemblage will appear as hundreds or thousands of fragmented olive stones in a concentrated deposit (see, for example, Smith, 1998; Margaritis and Jones, 2008; Rowan, 2015). The high degree of fragmentation is the result of crushing the olives prior to the pressing stage. Many of the olive stones will not survive combustion, especially when the pomace is subject to high temperatures such as those found inside a kiln. Consequently, a high concentration suggests largescale and/or repeat burning events and thus pomace fuel (Mason, 2007, p. 333; Warnock, 2007, p. 47). In the case of ritual or table waste, the assemblage is usually smaller and contains a greater quantity of intact stones despite lower burning temperatures increasing the chances of preservation. Reflectance measurements can also be used to confirm the use of olive pomace as a fuel and distinguish between the use of air-dried pomace and pomace that has been converted into charcoal (Braadbaart, Marinova and Sarpaki, 2016). 1.1 Current uses of pomace Today, 97% of the world’s olive oil is still made in the Mediterranean and in particular in Spain, Greece, Italy, Turkey, Morocco, and Tunisia (Christoforou and Fokaides, 2016; IOOC EU Olive Oil Figures 2018). Since 1990, EU production of olive oil has increased from 994,000 tonnes to 2.17 million tonnes or 2.36 million litres per annum (IOOC World Olive Oil Figures, 2018).1 As olive oil output increases so too does the volume of pomace. Although the modern twoand three-phase press extraction processes make pomace output more difficult to calculate, generating 2.36 million litres of oil results in the creation of approximately 4.13–4.72 million kg of pomace. Modern press methods differ from traditional methods in that they create a more mixed and chemically toxic pulp, especially the two-phase method where all the pomace and olive waste water are mixed together. Consequently, different treatment methods must be applied to the pomace prior to its utilization as a fuel (for a good overview of the different outcomes using traditional and modern presses, see Caputo et al., 2003 or Azbar et al., 2004). However, since the ratio of modern continuous presses to traditional presses varies by country, for simplicity, in this article, all pressing waste with a solid component will be called pomace regardless of water content. It is beyond the scope of this article to discuss the various uses and challenges associated with olive waste water, which does not contain the flesh or stones (Niaounakis, 2011). In the light of higher energy demands and a decreasing fossil fuel supply, in addition to the challenges associated with global warming, renewable and sustainable biomass fuels such as pomace are becoming ever more important. Unlike the combustion of fossil fuels, burning pomace 1 1 litre of olive oil weighs circa 0.92 kg (Marzano, 2013, p. 99). will not increase levels of atmospheric carbon dioxide and therefore not contribute to rising levels of greenhouse gasses. Any CO2 generated during combustion is offset by the continued presence of olive trees and other plant matter that photosynthesizes CO2 (Ali Rajaeifar et al., 2016, p. 87). Experiments have shown olive pomace to be a viable alternative to fossil fuels and unlike other biomass sources such as wheat or corn, the use of pomace does not act as competition for the food supply (Intini et al., 2011, p. 165). Throughout the Mediterranean and the Middle East pomace is still used in traditional ways. In Jordan and Syria, olive pomace is used to heat homes and cook food, while in Turkey it is used in bakeries and olive mills (Doymaz et al., 2004, p. 214; Azbar et al., 2004, p. 238; Warnock, 2007, p. 47–57; Rowan, 2015, p. 466). Other small-scale uses of pomace in Spain, Italy, Greece, Croatia and Slovenia include the heating of factories, private homes, and hotels, all of which make use of local resources (M.O.R.E., 2008). While these traditional small-scale uses of pomace remain important, a greater number of factories and hotels, for example, could take advantage of this resource. Unless local demand increases, pomace will continue to be generated in quantities that far outstrip local consumption. Governments, universities and research institutions have begun to dedicate considerable resources to developing more efficient ways to exploit this clean energy resource (Demicheli and Bontoux, 1996, p. 49–53; Arvanitoyannis, 2007; Vera et al., 2014; Christoforou and Fokaides, 2016; European Commission, 2017; M.O.R.E, 2018). Some of the major olive oil producing countries in the Mediterranean have started to make use of olive pomace fuel for various industrial activities and most commonly the generation of electric and thermal energy (Demicheli and Bontoux, 1996; García-Maraver et al., 2012). While today’s motivations are both financial and environmental, the drive to link industrial-scale, olive oil production with industrial-scale, energy generation is remarkably similar to the events that took place during the Roman period. 1.2 Olive oil production in Roman North Africa Roman conquest of the Mediterranean began in earnest in the 3rd century BC. By the late first century BC, Rome controlled all the land around the Mediterranean Sea and, in effect, all olive oil producing regions. Although olive oil was made in many parts of the Mediterranean prior to Roman hegemony, Roman territorial expansion brought about a significant expansion of olive groves, resulting in an increase in olive oil and pomace production (Mattingly, 1988a; 1988b). This expansion is no more readily apparent than in North Africa, which underwent an “olive boom” starting roughly in the 2nd century AD, and reaching its peak in the 3rd to 5th centuries AD (Mattingly, 1988a, p. 56; 1996, pp. 235–237; Hobson, 2015a, p. 148; 2015b, p. 219). The Romans invested significant capital in the planting of olive groves and the construction of presses along the Tunisian and Libyan coasts, as well as in the Tunisian Sahel (Figure 1). An even more dedicated investment can be seen in the planting IANSA 2018 ● IX/2 ● 147–156 Erica Rowan: Sustainable Fuel Practices in Roman North Africa and the Contemporary Mediterranean Basin 149 of enormous olive groves and the construction of hundreds of multi-presses sites in the Tunisian High Steppe and Libyan Djebel, semi-arid regions that only receive 200–300 mm of rainfall per annum (Mattingly, 1988a, pp. 44–45; 1996, pp. 236–237; Hobson, 2015a, p. 99). The successful planting and cultivation of these olive trees resulted in the output of millions of litres of oil. The territory around the three cities of Lepcis Magna, Sabratha and Oea in modern Libya, for example, may have been producing up to 30 million litres of oil per year (Mattingly, 1988a, p. 37). If olive oil was being produced on an industrial scale, so too was pomace (Mattingly, 1988a; 1988b; Hitchner, 2002). 2. Pomace use at Utica The site of Utica is located on the western side of the Mejerda estuary in northern Tunisia, 10 km from the coast (Hay et al., 2010, p. 325). Originally a Punic settlement, the earliest structures date to the 8th century BC. After the Roman defeat of Carthage in 146 BC, Utica was made the capital of the newly founded province of Africa. Although the city lost its capital status to Carthage after the Roman civil wars of the 1st century BC, it nevertheless continued to prosper as an important port centre and many public buildings associated with large Roman cities, such as baths, basilicas and theatres Figure 1. Coastal Tunisia and Libya with major sites and regions mentioned in the text (author). Figure 2. Area IV. The large lime kiln is visible at the top of the photo while smaller circular kiln 4022 is visible on the right-hand side. A rectangular cistern with rounded edges is located near the smaller kiln. Note the dark ash scatter near the lime kiln (photo courtesy of Andrew Wilson). IANSA 2018 ● IX/2 ● 147–156 Erica Rowan: Sustainable Fuel Practices in Roman North Africa and the Contemporary Mediterranean Basin 150 were constructed. During the imperial period it had the status of a municipium before achieving the higher rank of colonia under Hadrian. By the mid-3rd century it had become an important Christian centre. The city then declined during the Late Roman period and was captured by the Vandals in AD 439 and then the Byzantines in AD 534. Sometime between the early 5th and mid-6th centuries the alluvial fans in the es","PeriodicalId":38054,"journal":{"name":"Interdisciplinaria Archaeologica","volume":null,"pages":null},"PeriodicalIF":0.2000,"publicationDate":"2018-12-31","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"3","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Interdisciplinaria Archaeologica","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.24916/IANSA.2018.2.2","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q4","JCRName":"ANTHROPOLOGY","Score":null,"Total":0}
引用次数: 3

Abstract

As a readily available and renewable resource, olive pomace has been used as a fuel throughout the Mediterranean for centuries. This article will first discuss the extensive use of pomace fuel in Roman North Africa, introducing and adding the once coastal city of Utica to our growing list of sites with archaeobotanical evidence for pomace residue. The paper will then focus on the ways in which the Romans linked olive oil and pottery production. While environmental sustainability was unlikely to have been one of the Romans’ conscious objectives, the use of this fuel was vital to the continued production of North African ceramics, particularly in more arid areas. Today, in the face of increasing energy demands, pomace is once again being recognized as an important and sustainable resource. More work, however, still needs to be done to improve the efficiency of pomace use. The article will conclude by highlighting the valuable lessons that can be learned from ancient practices, especially the efficient pairing of olive cultivation and pottery production. IANSA 2018 ● IX/2 ● 147–156 Erica Rowan: Sustainable Fuel Practices in Roman North Africa and the Contemporary Mediterranean Basin 148 pomace fuel assemblages from olives burnt for ritual purposes or as table waste. In all cases, the burning, or carbonization process, turns the olive flesh and skin to ash and as a result we are often only left with burnt olives stones (endocarps) and occasionally the seeds. Usually a pomace assemblage will appear as hundreds or thousands of fragmented olive stones in a concentrated deposit (see, for example, Smith, 1998; Margaritis and Jones, 2008; Rowan, 2015). The high degree of fragmentation is the result of crushing the olives prior to the pressing stage. Many of the olive stones will not survive combustion, especially when the pomace is subject to high temperatures such as those found inside a kiln. Consequently, a high concentration suggests largescale and/or repeat burning events and thus pomace fuel (Mason, 2007, p. 333; Warnock, 2007, p. 47). In the case of ritual or table waste, the assemblage is usually smaller and contains a greater quantity of intact stones despite lower burning temperatures increasing the chances of preservation. Reflectance measurements can also be used to confirm the use of olive pomace as a fuel and distinguish between the use of air-dried pomace and pomace that has been converted into charcoal (Braadbaart, Marinova and Sarpaki, 2016). 1.1 Current uses of pomace Today, 97% of the world’s olive oil is still made in the Mediterranean and in particular in Spain, Greece, Italy, Turkey, Morocco, and Tunisia (Christoforou and Fokaides, 2016; IOOC EU Olive Oil Figures 2018). Since 1990, EU production of olive oil has increased from 994,000 tonnes to 2.17 million tonnes or 2.36 million litres per annum (IOOC World Olive Oil Figures, 2018).1 As olive oil output increases so too does the volume of pomace. Although the modern twoand three-phase press extraction processes make pomace output more difficult to calculate, generating 2.36 million litres of oil results in the creation of approximately 4.13–4.72 million kg of pomace. Modern press methods differ from traditional methods in that they create a more mixed and chemically toxic pulp, especially the two-phase method where all the pomace and olive waste water are mixed together. Consequently, different treatment methods must be applied to the pomace prior to its utilization as a fuel (for a good overview of the different outcomes using traditional and modern presses, see Caputo et al., 2003 or Azbar et al., 2004). However, since the ratio of modern continuous presses to traditional presses varies by country, for simplicity, in this article, all pressing waste with a solid component will be called pomace regardless of water content. It is beyond the scope of this article to discuss the various uses and challenges associated with olive waste water, which does not contain the flesh or stones (Niaounakis, 2011). In the light of higher energy demands and a decreasing fossil fuel supply, in addition to the challenges associated with global warming, renewable and sustainable biomass fuels such as pomace are becoming ever more important. Unlike the combustion of fossil fuels, burning pomace 1 1 litre of olive oil weighs circa 0.92 kg (Marzano, 2013, p. 99). will not increase levels of atmospheric carbon dioxide and therefore not contribute to rising levels of greenhouse gasses. Any CO2 generated during combustion is offset by the continued presence of olive trees and other plant matter that photosynthesizes CO2 (Ali Rajaeifar et al., 2016, p. 87). Experiments have shown olive pomace to be a viable alternative to fossil fuels and unlike other biomass sources such as wheat or corn, the use of pomace does not act as competition for the food supply (Intini et al., 2011, p. 165). Throughout the Mediterranean and the Middle East pomace is still used in traditional ways. In Jordan and Syria, olive pomace is used to heat homes and cook food, while in Turkey it is used in bakeries and olive mills (Doymaz et al., 2004, p. 214; Azbar et al., 2004, p. 238; Warnock, 2007, p. 47–57; Rowan, 2015, p. 466). Other small-scale uses of pomace in Spain, Italy, Greece, Croatia and Slovenia include the heating of factories, private homes, and hotels, all of which make use of local resources (M.O.R.E., 2008). While these traditional small-scale uses of pomace remain important, a greater number of factories and hotels, for example, could take advantage of this resource. Unless local demand increases, pomace will continue to be generated in quantities that far outstrip local consumption. Governments, universities and research institutions have begun to dedicate considerable resources to developing more efficient ways to exploit this clean energy resource (Demicheli and Bontoux, 1996, p. 49–53; Arvanitoyannis, 2007; Vera et al., 2014; Christoforou and Fokaides, 2016; European Commission, 2017; M.O.R.E, 2018). Some of the major olive oil producing countries in the Mediterranean have started to make use of olive pomace fuel for various industrial activities and most commonly the generation of electric and thermal energy (Demicheli and Bontoux, 1996; García-Maraver et al., 2012). While today’s motivations are both financial and environmental, the drive to link industrial-scale, olive oil production with industrial-scale, energy generation is remarkably similar to the events that took place during the Roman period. 1.2 Olive oil production in Roman North Africa Roman conquest of the Mediterranean began in earnest in the 3rd century BC. By the late first century BC, Rome controlled all the land around the Mediterranean Sea and, in effect, all olive oil producing regions. Although olive oil was made in many parts of the Mediterranean prior to Roman hegemony, Roman territorial expansion brought about a significant expansion of olive groves, resulting in an increase in olive oil and pomace production (Mattingly, 1988a; 1988b). This expansion is no more readily apparent than in North Africa, which underwent an “olive boom” starting roughly in the 2nd century AD, and reaching its peak in the 3rd to 5th centuries AD (Mattingly, 1988a, p. 56; 1996, pp. 235–237; Hobson, 2015a, p. 148; 2015b, p. 219). The Romans invested significant capital in the planting of olive groves and the construction of presses along the Tunisian and Libyan coasts, as well as in the Tunisian Sahel (Figure 1). An even more dedicated investment can be seen in the planting IANSA 2018 ● IX/2 ● 147–156 Erica Rowan: Sustainable Fuel Practices in Roman North Africa and the Contemporary Mediterranean Basin 149 of enormous olive groves and the construction of hundreds of multi-presses sites in the Tunisian High Steppe and Libyan Djebel, semi-arid regions that only receive 200–300 mm of rainfall per annum (Mattingly, 1988a, pp. 44–45; 1996, pp. 236–237; Hobson, 2015a, p. 99). The successful planting and cultivation of these olive trees resulted in the output of millions of litres of oil. The territory around the three cities of Lepcis Magna, Sabratha and Oea in modern Libya, for example, may have been producing up to 30 million litres of oil per year (Mattingly, 1988a, p. 37). If olive oil was being produced on an industrial scale, so too was pomace (Mattingly, 1988a; 1988b; Hitchner, 2002). 2. Pomace use at Utica The site of Utica is located on the western side of the Mejerda estuary in northern Tunisia, 10 km from the coast (Hay et al., 2010, p. 325). Originally a Punic settlement, the earliest structures date to the 8th century BC. After the Roman defeat of Carthage in 146 BC, Utica was made the capital of the newly founded province of Africa. Although the city lost its capital status to Carthage after the Roman civil wars of the 1st century BC, it nevertheless continued to prosper as an important port centre and many public buildings associated with large Roman cities, such as baths, basilicas and theatres Figure 1. Coastal Tunisia and Libya with major sites and regions mentioned in the text (author). Figure 2. Area IV. The large lime kiln is visible at the top of the photo while smaller circular kiln 4022 is visible on the right-hand side. A rectangular cistern with rounded edges is located near the smaller kiln. Note the dark ash scatter near the lime kiln (photo courtesy of Andrew Wilson). IANSA 2018 ● IX/2 ● 147–156 Erica Rowan: Sustainable Fuel Practices in Roman North Africa and the Contemporary Mediterranean Basin 150 were constructed. During the imperial period it had the status of a municipium before achieving the higher rank of colonia under Hadrian. By the mid-3rd century it had become an important Christian centre. The city then declined during the Late Roman period and was captured by the Vandals in AD 439 and then the Byzantines in AD 534. Sometime between the early 5th and mid-6th centuries the alluvial fans in the es
罗马北非和当代地中海盆地的可持续燃料实践
作为一种现成的可再生资源,几个世纪以来,橄榄渣一直被用作地中海地区的燃料。本文将首先讨论废渣燃料在罗马北非的广泛使用,介绍并将曾经的沿海城市尤蒂卡添加到我们不断增长的有废渣考古证据的遗址列表中。然后,本文将重点介绍罗马人将橄榄油与陶器生产联系起来的方式。虽然环境的可持续性不太可能是罗马人有意识的目标之一,但这种燃料的使用对北非陶瓷的持续生产至关重要,特别是在更干旱的地区。今天,面对日益增长的能源需求,垃圾再次被认为是一种重要的可持续资源。然而,要提高垃圾的利用效率,还需要做更多的工作。文章最后将强调从古代实践中可以学到的宝贵经验,特别是橄榄种植和陶器生产的有效结合。147-156 Erica Rowan:罗马北非和当代地中海盆地的可持续燃料实践148从用于仪式目的或作为餐桌废物燃烧的橄榄中提取的渣油燃料组合。在所有情况下,燃烧或碳化过程都会将橄榄的果肉和表皮变成灰烬,因此我们通常只剩下烧焦的橄榄核(内核),偶尔也会留下种子。通常,果渣组合在集中的沉积物中会出现数百或数千个破碎的橄榄石(例如,参见Smith, 1998;Margaritis and Jones, 2008;罗文,2015)。高度破碎是橄榄在压榨阶段之前被压碎的结果。许多橄榄石无法在燃烧中幸存下来,尤其是当渣滓处于高温下时,比如在窑中发现的高温。因此,高浓度表明大规模和/或重复燃烧事件,因此是渣滓燃料(Mason, 2007, p. 333;Warnock, 2007,第47页)。在仪式或餐桌废物的情况下,尽管较低的燃烧温度增加了保存的机会,但这些组合通常较小,含有更多的完整石头。反射率测量也可用于确认使用橄榄渣作为燃料,并区分使用风干渣和已转化为木炭的渣(Braadbaart, Marinova和Sarpaki, 2016)。今天,世界上97%的橄榄油仍然在地中海生产,特别是在西班牙、希腊、意大利、土耳其、摩洛哥和突尼斯(Christoforou和Fokaides, 2016;IOOC欧盟橄榄油数据2018)。自1990年以来,欧盟的橄榄油产量从99.4万吨增加到217万吨,即每年236万升(IOOC世界橄榄油数据,2018年)随着橄榄油产量的增加,果渣的数量也在增加。尽管现代的两阶段和三阶段压榨提取工艺使得渣滓产量更难计算,但产生236万升油的结果是产生大约413 - 472万公斤渣滓。现代压榨方法与传统压榨方法的不同之处在于,它们制造出更加混合和化学毒性更强的纸浆,尤其是将所有渣渣和橄榄废水混合在一起的两相压榨法。因此,在将渣滓用作燃料之前,必须采用不同的处理方法(关于使用传统和现代压力机的不同结果的良好概述,参见Caputo等人,2003年或Azbar等人,2004年)。然而,由于现代连续压榨机与传统压榨机的比例因国家而异,为简单起见,在本文中,无论含水量如何,所有含有固体成分的压榨废物都称为渣。讨论橄榄废水的各种用途和挑战超出了本文的范围,因为橄榄废水不含果肉或橄榄石(Niaounakis, 2011)。鉴于能源需求的增加和化石燃料供应的减少,除了与全球变暖相关的挑战外,可再生和可持续的生物质燃料(如渣滓)正变得越来越重要。与燃烧化石燃料不同,燃烧11升橄榄油的渣重约0.92千克(Marzano, 2013, p. 99)。不会增加大气中的二氧化碳含量,因此不会导致温室气体含量的上升。燃烧过程中产生的任何二氧化碳都被持续存在的橄榄树和其他光合作用二氧化碳的植物物质所抵消(Ali Rajaeifar等人,2016,第87页)。实验表明,橄榄渣是化石燃料的可行替代品,而且与小麦或玉米等其他生物质资源不同,橄榄渣的使用不会对食物供应构成竞争(Intini et al., 2011, p. 165)。 这座城市在罗马晚期衰落,公元439年被汪达尔人占领,公元534年被拜占庭人占领。在5世纪早期到6世纪中期之间的某个时候,在es的冲积扇
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Interdisciplinaria Archaeologica
Interdisciplinaria Archaeologica Arts and Humanities-Archeology (arts and humanities)
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