Jones J G
Freshwater Biological Association, The Ferry House, Ambleside, Cumbria LA22 0LP, United Kingdom.
Ecotoxicol Environ Saf. 2001 Oct;50(2):107-13. doi: 10.1006/eesa.2001.2079.
Before it is possible to predict the impact of human activities on the natural environment it is necessary to understand the forces that drive and, therefore, control that environment. This paper is concerned with the freshwater component of the aquatic environment. The driving forces involved (some of which are under man's control) can be divided into the physical and the chemical, but the response is, almost entirely, biological. Although most impacts of the food processing industry might be perceived to be on running waters, this is not always the case, but we can apply the same basic rules to both static and running waters. The physical forces that determine how a lake functions are as follows. In early spring, in the temperate zone, the temperature of the surface water in lakes rises and the sunlight input increases. This results in stratification of the water body. The cooler, deeper water is separated, physically, by gravity. This isolated water plays a very different role in the function of the lake and is analogous to how a river works. Man's activities drive these systems by our input of inorganic and organic substances. The inorganic inputs, particularly of phosphorous, stimulate undesirable algal growths, some of which may produce particularly dangerous toxins. We must now accept that climate change, driven by man, will exacerbate these problems. Organic inputs from the food industry, i.e., carbohydrates, lipids, and proteins, will all impact lakes and rivers by increasing the biological oxygen demand. The worst case scenario is total loss of oxygen from the water as a result of microbial activity. Lipids create the greatest oxygen demand but carbohydrates (more easily biodegradable) also result in unsightly "sewage fungus." Protein waste can be degraded to produce ammonia and sulfide, both of which produce toxicity problems. Bioremediation processes, particularly phytoremediation, can alleviate these problems in a cost-effective manner and this paper will address these options.
在预测人类活动对自然环境的影响之前,有必要了解驱动并因此控制该环境的各种力量。本文关注的是水生环境中的淡水部分。所涉及的驱动力(其中一些受人类控制)可分为物理和化学驱动力,但响应几乎完全是生物性的。尽管食品加工业的大多数影响可能被认为是对流动水体的影响,但情况并非总是如此,但我们可以将相同的基本规则应用于静态水体和流动水体。决定湖泊功能的物理力量如下。在温带地区的早春,湖泊表层水的温度升高,阳光输入增加。这导致水体分层。较冷、较深的水在重力作用下被物理分隔。这种隔离的水在湖泊功能中发挥着截然不同的作用,类似于河流的运作方式。人类活动通过输入无机和有机物质来驱动这些系统。无机物质的输入,尤其是磷的输入,会刺激有害藻类生长,其中一些可能产生特别危险的毒素。我们现在必须认识到,由人类驱动的气候变化将加剧这些问题。食品工业的有机物质输入,即碳水化合物、脂质和蛋白质,都会通过增加生物需氧量来影响湖泊和河流。最糟糕的情况是由于微生物活动导致水中氧气完全耗尽。脂质产生的需氧量最大,但碳水化合物(更易生物降解)也会导致难看的“污水真菌”。蛋白质废物可降解产生氨和硫化物,两者都会产生毒性问题。生物修复过程,特别是植物修复,可以以具有成本效益的方式缓解这些问题,本文将探讨这些选择。