中国农业科学 ›› 2021, Vol. 54 ›› Issue (18): 3919-3931.doi: 10.3864/j.issn.0578-1752.2021.18.011
龚世飞1(),丁武汉2,居学海3,肖能武1(),叶青松1,黄进1,李虎2()
收稿日期:
2020-11-06
接受日期:
2021-02-20
出版日期:
2021-09-16
发布日期:
2021-09-26
联系方式:
龚世飞,E-mail: gongsfsf@163.com。
基金资助:
GONG ShiFei1(),DING WuHan2,JU XueHai3,XIAO NengWu1(),YE QingSong1,HUANG Jin1,LI Hu2()
Received:
2020-11-06
Accepted:
2021-02-20
Published:
2021-09-16
Online:
2021-09-26
摘要:
【目的】对丹江口库区典型小流域农业面源污染现状进行调查分析,解析该地区农业面源污染负荷和污染源,以期为制定针对性防控策略及促进农业绿色发展提供参考依据。【方法】通过问卷调查形式对谭家湾流域进行实地走访调研,对两个村域内的种植、养殖和人居生活等污染源进行分类调查,应用输出系数法和等标污染负荷法对污染负荷进行估算。【结果】谭家湾流域农业面源污染实际产生量由2015年的162.32 t降低至2020年的27.79 t,等标污染负荷总量由62.44 m3下降至21.14 m3,主导污染源由土地利用转变为畜禽养殖。流域内总氮(TN)、总磷(TP)和化学需氧量(COD)的年负荷总量分别为5.56、0.86和21.37 t。各类污染源的贡献率表现为:畜禽养殖>土地利用>农村生活,其中生猪养殖的TN、TP和COD负荷量分别占流域负荷总量的50.91%、64.20%和46.66%,是该地区最重要的污染源。TN是流域内最主要的农业面源物,其污染等标负荷占负荷总量的52.6%,其次为TP,污染负荷率为40.7%,COD的等标污染负荷率最小为6.7%。环境污染风险评价结果显示,流域内畜禽粪便耕地负荷警报值为0.489,分级级数为Ⅱ,对环境构成污染的威胁为“稍有”,流域养殖总量在现有基础上还有10 815头猪当量的扩增空间。【结论】2015年以来,流域农业面源污染强度显著降低,保持合理的禽养殖规模,同时做好污染物消减措施,对促进丹江口库区典型流域农业面源污染持续减排具有重要意义。
龚世飞,丁武汉,居学海,肖能武,叶青松,黄进,李虎. 典型农业小流域面源污染源解析与控制策略——以丹江口水源涵养区为例[J]. 中国农业科学, 2021, 54(18): 3919-3931.
GONG ShiFei,DING WuHan,JU XueHai,XIAO NengWu,YE QingSong,HUANG Jin,LI Hu. Source Analysis and Control Strategies of Non-Point Source Pollution in Typical Agricultural Small Watershed: A Case Study of Danjiangkou Water Conservation Area[J]. Scientia Agricultura Sinica, 2021, 54(18): 3919-3931.
表1
各类污染物输出系数"
污染源 Pollutant source | 污染管控及处理措施 Pollution control and disposal measure | 污染物 Pollutant | |||
---|---|---|---|---|---|
TN | TP | COD | |||
每人生活污水 Rural sewage per person (kg·a-1) | 常规排放 Conventional emission | 0.57 | 0.058 | 23.36 | |
有水冲厕 Aqua privies | 2.04 | 0.45 | 13.87 | ||
无水冲厕 Dry latrine | 0.26 | 0.04 | 6.28 | ||
土地利用 Land use type (kg·hm-2·a-1) | 旱地 Dry land | 常规管理 Regular management | 25.56 | 1.79 | 18.00 |
保护性耕作、化肥农药等比例减量替代 Conservation tillage、Fertilizer, pesticide and other proportional reduction replacement | 3.77 | 0.38 | 5.92 | ||
林地 Woodland | 常规管理 Routine management | 3.05 | 0.16 | 32.50 | |
生草覆盖 Grass coverage | 0.69 | 0.08 | 3.37 | ||
园地 Garden | 常规管理 Normal management | 10.21 | 1.08 | 24.50 | |
保护性耕作、化肥农药等比例减量替代 Conservation tillage、Fertilizer, pesticide and other proportional reduction replacement | 4.56 | 0.53 | 2.84 | ||
单个畜禽养殖 A single livestock and poultry breeding (kg·a-1) | 猪 Pig | 水冲清粪 Water nightsoil | 0.49 | 0.08 | 4.91 |
干清粪 Dry nightsoil | 0.33 | 0.06 | 1.09 | ||
牛 Cow | 干清粪 Dry nightsoil | 1.17 | 0.03 | 7.96 | |
垫草垫料 Grass breeding | 0 | 0 | 0 | ||
家禽 Poultry | 水冲清粪 Water nightsoil | 0.012 | 0.015 | 0.275 | |
干清粪 Dry nightsoil | 0.004 | 0.007 | 0.120 | ||
羊 Sheep | 干清粪 Dry nightsoil | 0.230 | 0.045 | 0.440 | |
垫草垫料 Grass breeding | 0 | 0 | 0 |
表2
流域农业生产现状"
行政村 Villages | 常住人口 Resident population | 养殖规模 Farming scale (头/只) | 耕地面积 Agricultural acreage (hm2) | ||||||
---|---|---|---|---|---|---|---|---|---|
户数(户) Households | 人口(人) Population | 猪 Pig | 牛 Cow | 羊 Sheep | 家禽 Poultry | 旱地 Dry land | 林地 Woodland | 园地 Garden | |
五道岭 Wudaoling | 435 | 685 | 283 | 210 | 525 | 3117 | 141.26 | 980.67 | 38.67 |
圩坪寺 Weipingsi | 386 | 579 | 8231 | 67 | 212 | 2649 | 106.52 | 904.00 | 18.67 |
合计 Total | 821 | 1264 | 8514 | 277 | 737 | 5766 | 247.78 | 1884.67 | 57.34 |
表3
流域农业面源污染物负荷贡献"
行政村 Village | 污染物 Pollutant | 农村生活 Rural life (t·a-1) | 畜禽养殖 Livestock and poultry breeding (t·a-1) | 土地利用类型 Land use type (t·a-1) | 合计 Total (t·a-1) | 贡献率 Percent (%) | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
猪 Pig | 牛 Cow | 羊 Sheep | 家禽 Poultry | 旱地 Dry land | 林地 Woodland | 园地 Garden | ||||||||||
五道岭 Wudaoling | TN | 0.14 | 0.09 | - | - | 0.01 | 0.53 | 0.68 | 0.18 | 1.63 | 29.33 | |||||
TP | 0.03 | 0.02 | - | - | 0.02 | 0.05 | 0.08 | 0.02 | 0.22 | 25.35 | ||||||
COD | 1.89 | 0.31 | - | - | 0.37 | 0.84 | 3.30 | 0.11 | 6.82 | 31.91 | ||||||
圩坪寺 Weipingsi | TN | 0.10 | 2.72 | - | - | 0.01 | 0.40 | 0.62 | 0.08 | 3.93 | 70.67 | |||||
TP | 0.02 | 0.49 | - | - | 0.02 | 0.04 | 0.07 | 0.00 | 0.64 | 74.65 | ||||||
COD | 1.53 | 8.97 | - | - | 0.32 | 0.63 | 3.05 | 0.05 | 14.55 | 68.09 | ||||||
合计 Total (t·a-1) | TN | 0.24 | 2.81 | - | - | 0.02 | 0.93 | 1.30 | 0.26 | 5.56 | 100.00 | |||||
TP | 0.05 | 0.51 | - | - | 0.04 | 0.09 | 0.15 | 0.02 | 0.86 | 100.00 | ||||||
COD | 3.42 | 9.28 | - | - | 0.69 | 1.47 | 6.35 | 0.16 | 21.37 | 100.00 | ||||||
贡献率 Percent (%) | TN | 4.34 | 50.55 | - | - | 0.36 | 16.71 | 23.36 | 4.67 | 100.00 | ||||||
TP | 5.45 | 59.53 | - | - | 4.67 | 10.51 | 17.51 | 2.33 | 100.00 | |||||||
COD | 16.00 | 43.43 | - | - | 3.23 | 6.88 | 29.72 | 0.75 | 100.00 |
表4
流域农业面源污染物负荷总量"
年份 Year | 污染物 Pollutant | 农村生活 Rural life (t·a-1) | 畜禽养殖 Livestock and poultry breeding (t·a-1) | 土地利用类型 Land use type (t·a-1) | 合计 Total (t·a-1) | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
猪 Pig | 牛 Cow | 羊 Sheep | 家禽 Poultry | 旱地 Dry land | 林地 Woodland | 园地 Garden | |||||||||
2015 | TN | 0.72 | 4.17 | 0.33 | 0.17 | 0.07 | 6.33 | 5.75 | 0.59 | 18.12 | |||||
TP | 0.07 | 0.68 | 0.00 | 0.02 | 0.09 | 0.44 | 0.30 | 0.06 | 1.67 | ||||||
COD | 29.53 | 41.80 | 2.18 | 0.32 | 1.59 | 4.46 | 61.25 | 1.40 | 142.53 | ||||||
2020 | TN | 0.24 | 2.81 | - | - | 0.02 | 0.93 | 1.30 | 0.26 | 5.56 | |||||
TP | 0.05 | 0.51 | - | - | 0.04 | 0.09 | 0.15 | 0.02 | 0.86 | ||||||
COD | 3.42 | 9.28 | - | - | 0.69 | 1.47 | 6.35 | 0.16 | 21.37 |
表5
流域等标污染负荷特征"
污染物 Pollutant | 负荷系数 Load factor | 行政村Village | 污染源 Pollutant source | Pin (m3·a-1) | Kin | |||
---|---|---|---|---|---|---|---|---|
五道岭 Wudaoling | 圩坪寺 Weipingsi | 农村生活 Rural life | 畜禽养殖 Livestock and poultry breeding | 土地利用 Land utilization | ||||
TN | P1i (m3) | 3.26 | 7.86 | 0.480 | 5.660 | 4.980 | 11.12 | |
K1i | 0.29 | 0.71 | 0.043 | 0.509 | 0.448 | 0.526 | ||
TP | P1i (m3) | 2.20 | 6.40 | 0.500 | 5.500 | 2.600 | 8.60 | |
K1i | 0.26 | 0.74 | 0.058 | 0.640 | 0.302 | 0.407 | ||
COD | P1i (m3) | 0.45 | 0.97 | 0.230 | 0.660 | 0.530 | 1.42 | |
K1i | 0.32 | 0.68 | 0.161 | 0.465 | 0.375 | 0.067 | ||
Pnj (m3·a-1) | 5.91 | 15.23 | 1.208 | 11.820 | 8.112 | P=21.14 | ||
Knj | 0.28 | 0.72 | 0.057 | 0.559 | 0.384 |
表6
流域农业面源污染等标负荷总量"
年份 Year | 污染物 Pollutant | 农村生活 Rural life (t·a-1) | 畜禽养殖 Livestock and poultry breeding (t·a-1) | 土地利用类型 Land use type (t·a-1) | 合计 Total (t·a-1) | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
猪 Pig | 牛 Cow | 羊 Sheep | 家禽 Poultry | 旱地 Dry land | 林地 Woodland | 园地 Garden | |||||||||
2015 | TN | 1.44 | 8.34 | 0.66 | 0.34 | 0.14 | 12.66 | 11.50 | 1.18 | 36.24 | |||||
TP | 0.70 | 6.80 | 0.00 | 0.20 | 0.90 | 4.40 | 3.00 | 0.60 | 16.70 | ||||||
COD | 1.97 | 2.79 | 0.15 | 0.02 | 0.11 | 0.30 | 4.08 | 0.09 | 9.50 | ||||||
2020 | TN | 0.48 | 5.62 | - | - | 0.04 | 1.86 | 2.60 | 0.52 | 11.12 | |||||
TP | 0.50 | 5.10 | - | - | 0.40 | 0.90 | 1.50 | 0.20 | 8.60 | ||||||
COD | 0.23 | 0.62 | - | - | 0.05 | 0.10 | 0.42 | 0.01 | 1.42 |
表7
流域畜禽粪便负荷警报值及环境风险"
畜禽种类 Livestock | 粪便量 Manure (×104 t·a-1) | 猪粪当量转换系数 Equivalency factor | 猪粪当量 Pig fecal equivalent | 合计 Total (×104 t·a-1) | 耕地负荷量 Cultivated land load (×t·hm-2·a-1) | 警报值 Alarm value | 分级指数 Classification | 对环境构成污染的威胁 Environmental risk | |||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
猪Pig | 0.955 | 1.00 | 0.955 | 1.168 | 14.676 | 0.489 | Ⅱ | 稍有 Slightly | |||||
牛Sheep | 0.233 | 0.50 | 0.116 | ||||||||||
羊Cow | 0.064 | 1.03 | 0.066 | ||||||||||
家禽Poultry | 0.025 | 1.21 | 0.031 |
表8
流域畜禽养殖环境容量及实际总量"
承载力 Carrying capacity (t) | 环境容量(猪当量) Environmental capacity (Equivalent based on pig) | 50%理论养殖量(猪当量) 50% theoretical breeding quantity (Equivalent based on pig ) | 实际养殖量(猪当量) Actual amounts of livestock (Equivalent based on pig) | 污染风险指数 Pollution risk index | |
---|---|---|---|---|---|
以N计 Equivalent based on nitrogen | 18.258 | 55328 | 27664 | 16849 | 0.609 |
以P计 Equivalent based on phosphorus | 3.759 | 62650 | 31325 | 14334 | 0.458 |
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