Scientia Agricultura Sinica ›› 2020, Vol. 53 ›› Issue (18): 3752-3763.doi: 10.3864/j.issn.0578-1752.2020.18.011

• SOIL & FERTILIZER·WATER-SAVING IRRIGATION·AGROECOLOGY & ENVIRONMENT • Previous Articles     Next Articles

Nitrogen and Phosphorus Loads and Their Environmental Effects of Animal Manure in Hainan Island from 1988 to 2018

DING Shang1(),FU Yang2,GUO HaoHao1,SONG ChenYang1,LI BoLing3,ZHAO HongWei1()   

  1. 1College of Ecology and Environment, Hainan University/Key Laboratory of A&F Environmental Processes and Ecological Regulation of Hainan Province/Center for Eco-Environmental Restoration Engineering of Hainan Province, Haikou 570228
    2College of Animal Science and Technology, Hainan University, Haikou 570228
    3Animal Husbandry Technology Station of Hainan Province, Haikou 570100
  • Received:2019-12-13 Accepted:2019-12-30 Online:2020-09-16 Published:2020-09-25
  • Contact: HongWei ZHAO E-mail:Dshainu@163.com;hwzhao@hainu.edu.cn

Abstract:

【Objective】The objective of this study is to reveal the flow characteristics of nitrogen (N) and phosphorus (P) in manure and their effects to the environment during the development of livestock and poultry breeding in Hainan, and to provide references for regional agricultural development planning and adjustment of livestock and poultry breeding structure. 【Method】Based on the statistical data and literature data, the nutrient yield of animal manure and nutrient carrying capacity per unit cultivated area in Hainan Island from 1988 to 2018 were estimated, and their effects to the environment were deeply analyzed by using alarm value and environmental risk index. When the alarm value is less than 0.4, it can be considered as no threat to the environment, and when the environmental risk index is below 1.00, the risk to the environment can be ignored, above these safety values will have different degrees of impacts on the environment. 【Result】From 1988 to 2018, the changes of the animal manure amount in Hainan Island experienced three stages. The total amount of animal manure increased from 1988 to 2005, and decreased a lot from 2006 to 2008. Since then it developed slowly and stabilized, and the amount of animal manure produced in 2018 was 10.50×106t. In terms of nutrient yield, the annual variation trends of nitrogen and phosphorus were similar, with the largest yield in 2005 and a relatively large decline in 2006. To 2018, the yields of nitrogen and phosphorus in manure were 7.41×104 and 1.01×104 t, respectively. The nitrogen and phosphorus loads per unit cultivated land area also experienced a stable trend after continuous increasing. To 2018, cultivated land nitrogen load was 168.80 kg·hm-2, and cultivated land phosphorus load was 23.05 kg·hm-2. In 2018, regional variations were relatively large. The nitrogen and phosphorus loads per unit cultivated area were higher in eastern and northern regions, while lower in western and central regions. The highest nitrogen and phosphorus loads were Dingan (288.50 and 40.35 kg·hm-2, respectively), and the lowest were Dongfang (61.66 and 8.83 kg·hm-2, respectively). In terms of environmental effects, the alarm values of animal manure per cultivated land from 1988 to 2018 were always at high levels, most years between 1.0 to 1.5, which belonged to the classification standard of IV level and had a serious threat to the environment. In 2018, the alarm values in Dingan and Chengmai were 2.66 and 4.59 (reached the VI level), which had a serious threat to the environment, while only Dongfang was at a safe level with the alarm value of 0.36, which reached the I level. According to the environmental risk assessment results, the environmental risk of animal manure in cultivated land in Hainan Island was relatively high. In recent years, with the total amount of animal breeding reduction, the environmental risk indexes in 2018 dropped to 1.99 (N) and 1.32 (P), respectively. At the regional level, for nitrogen pollution, the environmental risk index of Dingan was the highest (3.39), while the lowest (0.73) was Dongfang; for phosphorus pollution, the environmental risk index in Dongfang (0.50) was the lowest in 2018, which can be considered that phosphorus in Dongfang had a low potential threat to the environment, while Dingan had a serious impact on the environment, with a value as high as 2.31. In general, both the alarm value and the environmental risk index indicated that the potential environmental risk of animal manure pollution in Hainan Island was serious, from the perspective of spatial distribution, environmental risks in eastern cities and counties such as Dingan and Wanning were higher than those in western regions such as Lingao and Dongfang, and most cities and counties posed a higher degree of threat to the environment. 【Conclusion】Due to the influence of animal breeding scale and cultivated land area, the nitrogen load per cultivated land area in Hainan Island is relatively high, and the potential environmental risks of the region scales cannot be ignored. Therefore, the future development plan of livestock and poultry breeding in Hainan Island should focus on the control of pollutants, regional distribution and management, meanwhile, realize the utilization of animal manure resources and the green development of Hainan Island by reducing the animal manure discharge to the environment and adopting resource recycling modes.

Key words: Hainan Island, animal manure, loads of nitrogen and phosphorus, environmental effect

Table 1

Animal manure parameters and their nutrient contents"

畜禽种类
Animal category
鲜重
Fresh weight (kg)
生长周期
Growth period (d)
粪尿产生量
Manure production (kg·d-1)
氮素产生量
N production (g·d-1)
磷素产生量
P production (g·d-1)
猪Pig 90 199 3.74 36.43 4.83
奶牛Dairy cattle 624 365 50.99 353.41 62.46
肉牛Beef cattle 316 365 23.02 65.93 10.52
役用牛Draft cattle 328 365 27.63 139.76 25.99
羊Sheep 35 365 0.87 2.15 0.46
肉鸡Chicken 2 80 0.06 0.71 0.06
蛋鸡Egg-laying hen 2 365 0.12 1.16 0.23
鸭Duck 2 210 0.06 0.71 0.06
鹅Goose 4 120 0.06 0.71 0.06

Fig. 1

Changes of manure emissions and nutrient production in Hainan Island from 1988 to 2018"

Fig. 2

Loads of total nitrogen and phosphorus in unit cultivated land of Hainan Island from 1988 to 2018 “—” means the limited amount of total nitrogen application, “” means the limited amount of total phosphorus application。下同 The same as below"

Fig. 3

Loads of total nitrogen and phosphorus in unit cultivated land area in Hainan Island in 2018"

Fig. 4

Pig manure equivalent load and alarm value in Hainan Island from 1988 to 2018"

Table 2

Pig manure equivalent load and the classification of threat to the environment of Hainan in 2018"

地区
Area
猪粪当量
Pig manure equivalent (×104 t)
畜禽粪尿负荷量
Load of manure (t·hm-2·a-1)
预警值
Alarm value (R)
预警级别
Classification level
对环境的威胁程度
The threat to environment
海口Haikou 159.61 32.67 0.73 有Medium
三亚Sanya 55.48 38.15 0.85 有Medium
五指山Wuzhishan 14.37 43.93 0.98 有Medium
文昌Wenchang 233.28 58.47 1.30 较严重Less serious
琼海Qionghai 176.86 76.73 1.71 严重Serious
万宁Wanning 188.79 98.21 2.18 严重Serious
定安Dingan 264.48 119.48 2.66 很严重More serious
屯昌Tunchang 103.73 77.51 1.72 严重Serious
澄迈Chengmai 631.61 206.37 4.59 很严重More serious
临高Lingao 75.57 23.75 0.53 稍有Slight
儋州Danzhou 143.13 27.72 0.62 稍有Slight
东方Dongfang 75.51 16.39 0.36 无None
乐东Ledong 115.36 38.08 0.85 有Medium
琼中Qiongzhong 28.71 28.66 0.64 稍有Slight
保亭Baoting 29.18 48.57 1.08 较严重Less serious
陵水Lingshui 48.05 40.68 0.90 有Medium
白沙Baisha 30.61 26.29 0.58 稍有Slight
昌江Changjiang 58.12 24.60 0.55 稍有Slight

Fig. 5

Feeding capacity, actual amounts and environmental risk index of livestock and poultry in Hainan Island from 1988 to 2018"

Table 3

Feeding capacity, actual amounts and environmental risk index of livestock and poultry of different areas in 2018"

地区
Area
承载力
Loading capacity (t)
养殖容量(万头猪当量)
Feeding capacity
实际养殖量(万头猪当量)
Actual amounts
环境风险指数
Environmental risk index
N P N P N P N P
海口Haikou 8305 1710 62.46 96.99 55.44 56.07 1.78 1.16
三亚Sanya 2472 509 18.59 28.87 20.66 21.29 2.22 1.48
五指山Wuzhishan 556 115 4.18 6.50 5.30 5.53 2.53 1.70
文昌Wenchang 6782 1396 51.01 79.21 48.09 46.45 1.89 1.17
琼海Qionghai 3918 807 29.47 45.76 39.31 35.66 2.67 1.56
万宁Wanning 3268 673 24.58 38.16 40.09 41.81 3.26 2.19
定安Dingan 3763 775 28.30 43.94 48.03 50.66 3.39 2.31
屯昌Tunchang 2275 468 17.11 26.57 26.92 28.92 3.15 2.18
澄迈Chengmai 5203 1071 39.13 60.76 62.04 60.99 3.17 2.01
临高Lingao 5410 1114 40.69 63.18 18.74 19.76 0.92 0.63
儋州Danzhou 8777 1807 66.01 102.51 60.58 60.13 1.84 1.17
东方Dongfang 7834 1613 58.92 91.49 21.37 23.09 0.73 0.50
乐东Ledong 5149 1060 38.73 60.14 36.68 43.17 1.89 1.44
琼中Qiongzhong 1703 351 12.81 19.88 11.24 11.74 1.76 1.18
保亭Baoting 1021 210 7.68 11.93 11.09 11.32 2.89 1.90
陵水Lingshui 2008 413 15.10 23.45 19.90 23.29 2.63 1.99
白沙Baisha 1979 408 14.89 23.12 11.95 11.85 1.61 1.03
昌江Changjiang 4016 827 30.20 46.90 19.41 21.80 1.29 0.93
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