GEOGRAPHICAL RESEARCH ›› 2016, Vol. 35 ›› Issue (11): 2025-2040.doi: 10.11821/dlyj201611003
• Trends in Geography • Previous Articles Next Articles
Xuegang GONG1,2(), Xiaoyong LIAO1(
), Xiulan YAN1, You LI1,2, Kun YANG1,2, Dan ZHAO1
Received:
2016-03-24
Revised:
2016-07-28
Online:
2016-11-25
Published:
2016-11-24
Xuegang GONG, Xiaoyong LIAO, Xiulan YAN, You LI, Kun YANG, Dan ZHAO. Measures on soil baseline determination for environmental damage identification and assessment[J].GEOGRAPHICAL RESEARCH, 2016, 35(11): 2025-2040.
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Tab. 1
The methods of baseline determination for environmental damage identification and assessment"
方法 | 依据 | 工作步骤 | 优点 | 缺点 |
---|---|---|---|---|
历史数据法 | 受损害区域历史信息 | 基础调研→历史数据收集→数据筛选、分析和评估→确定基线 | 损害评估结果 准确 | 受历史数据资料限制,较难直接应用 |
参考点位法 | 相似条件未受污染的参考区域数据 | 基础调研→选定参考点位或区域→深入调查分析→确定基线 | 直接、客观 | 需对参考区域开展大量和长期的调查分析 |
环境标准法 | 环境标准值 | 基础调研→相关环境标准比较分析→确定基线 | 简单、方便 | 部分现行标准难以满足实际应用需要 |
模型推算法 | 模型 | 基础调研→数据收集→模型构建和优化→深入调查、 分析和评估→基线水平预测和确定 | 易于控制,可将现象简化、放大或缩小 | 需要大量数据,模型不确定性程度难以确定, 且可用模型较少 |
Tab. 2
The cases of baseline determination for environmental damage assessment in the USA"
序号 | 地点 | 事件描述 | 方法 | 基线水平 |
---|---|---|---|---|
1 | Hudson River Superfund site | 位于Fort Edward 和 Hudson Falls的两家通用电气制造厂 向河流中排放了近590 t的PCBs,对Hudson River造成了严重的污染损害, 为有效评估自然资源损害,受托人组织开展了NRDA | 历史数据法、环境标准法 | 土壤:2.5 mg·kg-1 沉积物:1.7 mg·kg-1 鱼类:2 mg·kg-1 |
2 | Gowanus Canal Superfund site | Gowanus Canal是通往纽约港的主要商业路线, 沿线工厂的生产活动排放了大量的污染物, 包括PAHs、PCBs、重金属、VOCs等, 对沉积物、生物资源等造成了严重损害 | 环境标准法、参考点位法 | 沉积物:1.58 μg·kg-1(DDT) 生物资源:58.3 μg·kg-1(PAHs) |
3 | Buffalo River Superfund site | 由于历史发展,工业活动以及船舶活动, 有害物质和石油污染对河流及其河岸资源造成严重的污染损害 | 环境标准法、历史数据法 | 沉积物:1.6 mg·kg-1(TEC,PAHs) 地下水:5 μg·L-1(甲苯、二甲苯) |
4 | Eagle Harbor Superfund site | 20世纪早期,Wyckoff公司旗下的木材处理厂和造船厂产生的PAHs、 汞和其他重金属污染物,严重损害区域地下水、 土壤和沉积物等自然资源 | 环境标准法 | 沉积物:0.4 mg·kg-1(As) 生物资源:0.0026 mg·kg-1、0.0006 mg·kg-1 (As、PCBs) |
5 | Lower Duwamish River Superfund site | 20世纪初期开始,沿岸工业和商业设施排放了大量有毒有害物质HCB ,给鱼类、鸟类、野生动物及其栖息地造成了严重的污染损害 | 环境标准法 | 生物资源:22 μg·kg-1 |
6 | Blackbird Mine Site | 矿业活动排放了大量的含重金属Cu和Co污染物的废水, 导致地表水资源受到严重污染损害 | 对照点位法 | |
7 | Iron Mountain Mine | 历史采矿行动中采用酸浸出法, 导致大量的酸性矿井排水进入到周边地表水环境中, 造成了严重的污染损害影响 | 环境标准法、参考点位法 | |
8 | Kerr-McGee Chemical Corp | 该工厂场地主要用于杂酚油木材前期处理,并于1974年停产, 但存放的杂酚油和污泥持续产生挥发性有机物, 特别是PAHs,严重影响区域环境 | 历史数据法 | 沉积物:1.61 mg·kg-1 (Threshold Effects Concentration) 沉积物:22.8 mg·kg-1 (Probable Effects Concentration) |
9 | Kalamazoo River | 在对无碳复写纸进行回收的过程中释放了大量的PCBs物质到河流中, 导致沉积物、地表水和鱼中的PCBs浓度严重超标 | 参考点位法、环境标准法 | 地表水:0.008 μg·L-1(2000-2001年) 地表水:0.014 μg·L-1(保护水生生物) |
10 | DuPont Newport | 该工厂场地最早用于无机颜料的生产, 后又用以生产有机颜料及二氧化铬等物质, 造成严重的污染损害影响 | 模型推算法 |
Tab. 4
Available soil standards for baseline determination in China"
国家/地区 | 年份 | 名称 | 功能 | 保护对象 | 污染物数量 | 主要污染物 |
---|---|---|---|---|---|---|
中国 | 1995 | 土壤环境质量标准 | 土壤评价 | 生态 背景 | 10 | As、Cd、Cr、DDT、六六六等 |
中国台湾 | 2001 | 土壤污染管制标准 | 土壤评价 | 健康 | 39 | Cr、Cd |
中国 | 2006 | 温室蔬菜产地环境质量评价标准 | 土壤评价 | 生态 | 11 | As、Cd、Cr、Hg、Pb、DDT、六六六等 |
中国香港 | 2006 | 基于风险的土壤整治标准 | 场地修复 | 健康 | 54 | As、Cr(VI)、PAHs、PCBs、氰化物等 |
中国 | 2006 | 食用农产品产地环境质量评价标准 | 土壤评价 | 生态 | 12 | As、Cd、Cr、Cu、Pb、DDT、六六六等 |
中国 | 2007 | 展览会用地土壤环境质量评价标准(暂行) | 土壤评价 | 健康 | 92 | As、Cd、PAHs、PCBs、DDT、总石油烃等 |
中国北京 | 2011 | 场地土壤环境风险评价筛选值 | 风险评价 | 健康 | 88 | As、Cr(VI)、氰化物、PAHs、PCBs等 |
Tab. 5
Soil environment quality standards in other countries"
国家/地区 | 时间 | 名称 | 功能 | 保护对象 | 污染物数量 | 主要污染物 |
---|---|---|---|---|---|---|
日本 | 1975 | 农用地土壤环境污染防治法 | 防治农田污染 | 健康 | 3 | As、Cd、Cu |
美国 | 1996 | Soil Screening Guidance | 风险评估 | 健康 | 706 | As、Cr(VI)、PAHs、PCBs、DDT等 |
荷兰 | 2000 | Soil Quality Standards | 土壤评价 | 生态 | 76 | As、Cd、Cr、Cu、PAHs、DDT等 |
英国 | 2002 | Soil Guideline Value | 风险评价 | 健康 | >70 | As、Cd、Hg、苯、苯酚、PCBs等 |
美国 | 2003 | Ecological Soil Screening Levels | 风险评估 | 生态 | 24 | As、Cd、Cr、Pb、狄氏剂、TNT、DDT等 |
日本 | 2010 | 土壤污染对策法 | 土壤评价 | 健康 | 25 | As、Cd、TCE、PCB、苯、农药等 |
加拿大 | 2007 | Soil Quality Guideline | 风险评估 | 健康 生态 | 32 | As、Cd、Cr、DDT、PCBs、PCDD等 |
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