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Introduction
引言
Pterocarpus santalinusL.f.(Red Sanders) is a narrowly endemic species naturally distributed over anarea of about 0.4 million ha mainly in the hilly tracts in Chittoor, Cuddappah,Nellor, Prakasam and Kurnool districts of Andhra Pradesh(IFGTB2011). Thespecies occurs in ‘Dry Red Sanders-Bearing Forest’ which is classified as‘5A/C2 Forest Type’(Champion and Seth 1968). Red Sanders is highly valued forits heavy, dark claret-red heartwood which is yield 16% of red coloring matterto santalin, a natural dye used to color liquors, pharmaceutical preparations,food stuffs, etc. (Ramakrishna 1962; Anuradha and Pullaiah 1998). It isrenowned for its characteristic timber of exquisite color, beauty andsuperlative technical qualities and ranks among the finest luxury wood in theworld which is highly useful for making high-value musical instruments,cabinets, ornamental veneers, toys, dolls and was used in incense.
檀香紫檀在自然界仅分布在安得拉邦的Chittoor、 Cuddappah、 Nellor、Prakasam 和 Kurnool等地总面积约40万公顷的山区。……紫檀因其沉重的深红色心材而价值高昂,含有16%的红色色素,是一种可用于酒类、药物和食品的天然色素(Ramakrishna 1962; Anuradha and Pullaiah 1998)。它以其特有的色泽、美观和良好工艺性的木材而闻名,是世界上最高级的奢侈品木材之一,用于制作高价乐器、柜子、装饰面板、饰品、玩具和熏香。
The Red Sandersis under severe threat in its native range, owing to its endemism to smallarea, poor regeneration and overexploitation due to illegal felling. Despite aban on felling and sale, good-quality Red Sanders are illegally traded sincethey fetch very high price in the global market. Based in the grain type, theRed Sanders trees may be divided into two types in commerce, viz. wavy-grainedand straight-grained which occur mixed in the forest or plantation (Lohidas andDayanand 1984; Dayanand and Lohidas 1988). The wavy-grained variants arepreferred in the global markets and fetch higher price compared tonormal-grained types. State Forest Department of Tamil Nadu, Kerala and AndhraPradesh have raised Red Sanders plantations in several locations other than itsnatural ranges during last 50 years. A few number of tree growers and farmersare also cultivating this species in farm land in Andhra Pradesh, Tamil Nadu,Orissa and Karnataka and in other states, and about 3000 ha of Red Sandersplantations currently exists (IFGTB 2011).
紫檀在自然界受到严重威胁,源于其狭窄的分布区域、缓慢的更新速度和非法采伐。尽管有禁止采伐和买卖的禁令,优质紫檀仍因其在国际市场的高价而被非法贸易。根据纹理种类,紫檀树在贸易中可分为波纹和直纹两种,在森林和种植园中均有出现(Lohidas and Dayanand 1984; Dayanand andLohidas 1988)。与直纹相比,波纹在国际市场上更受欢迎,价格更高。在过去的50年中,泰米尔纳德邦,喀拉拉邦和安得拉邦的森林管理部门在天然林区之外的若干地方建立了紫檀种植园。在安得拉邦、泰米尔纳德邦、奥里萨邦、卡纳塔克邦以及其它邦,也有一些植树者和农民在田野中种植紫檀树,目前约有3000公顷的紫檀种植面积(IFGTB 2011)。
Through growthrate is reported to be faster under plantations raised in rich soils comparedto natural population(ICFRE 1992), not much information is available regardinggrowth rate of the species according to location, climate and soil outside itsnatural range. The heartwood is the main economics part of the tree in RedSanders. Information regarding extent of formation of heartwood and quality ofheartwood in Red Sanders plantations compared to its natural range is also notavailable. In this backdrop, the current study was conducted to evaluate thevariation in heartwood, sapwood and bark content, and wood density ofplantation-grown Red Sanders trees of various age classes grown in variouslocations across southern India.
虽然有报道称,种植于肥沃土壤的人工林生长速度比天然林快(ICFRE1992),但是该物种在人工环境下生长速度与地理位置、气候和土壤的关系,并无多少信息。心材是紫檀的主要价值所在。人工林在心材构成和质量方面与天然林对比的信息也没有。在此背景下,本研究对印度南部不同地方不同年龄的紫檀人工林的心材、边材、树皮比例和木材密度进行评估。