Chemical 物质 Management
通过适当控制和减少化学物质的排放，尽量减少对环境的影响
While chemical substances make people’s lives more convenient, they also could have harmful effects on the environment or on human beings. 因此, we believe that taking into consideration product safety, occupational safety and health, 而通过妥善管理化学物质对环境造成的影响是一项重要的责任.
Since fiscal 1999, 娱乐大发澳门赌博平台除了实施产品环境影响评估系统等措施外，还制定并努力实现自己的减少排放和化学物质转移的目标*1 and the Green Procurement 系统*2. 定期, we also review chemical substances, 根据有关法律法规的制定和修改.
2023财年, 十大赌博娱乐平台将继续从事彻底的化学物质管理活动，意识到必须尽量减少其影响.
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*1产品环境影响评估系统:从原材料采购到生产的所有阶段，评估产品对环境影响的系统, 使用, 处理, and transportation.
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*2绿色采购系统:在采购原材料时优先考虑对环境影响较低的系统, 部分, 等.
- 11-92
Reduce the impact of chemical substances
Aim: Reduce chemical emission and transport volumes
Indicator VOC emissions (Japan)
当前中期管理计划(2020-2022)目标-3% 2022财年业绩-17.1％ (compared with fiscal 2019)
For details, see 环境al Management Promotion 系统.
Controlling VOC的排放
娱乐大发澳门赌博平台的中期目标是，与2019财年报告的水平相比，将VOC排放量减少3%或更多. In fiscal 2022, VOC emissions in Japan decreased by 17.1% compared with fiscal 2019.
Preventing Air and Water Pollution
娱乐大发澳门赌博平台遵守废气和水排放相关设备的法律法规.
Soil Contamination Countermeasures
娱乐大发澳门赌博平台对其所有生产基地的土壤污染进行了自愿评估. 在完成向政府提交的报告的同时，集团已在发现污染的所有地点实施了清理措施和努力，旨在防止进一步污染. 此外，集团持续监测地下水，确认污染没有扩散.
此外, 本集团在出售已关闭生产设施的土地时采取法律规定的净化措施. In fiscal 2022, conditions did not require any new measures to be taken.
含多氯联苯设备的处置和储存以及使用氟碳的设备的管理
含多氯联苯的变压器和电容器正在被依次拆除，因为多氯联苯处理设施已准备好接受十大赌博娱乐平台的设备. Control of equipment containing PCBs in storage is strictly enforced, including locking of storage facilities and periodic inspections.
正在采取步骤，根据日本的《十大赌博娱乐平台》(《十大赌博娱乐平台》)，提高人们对有关使用氟化碳的设备的强制性要求的认识，并确保进行彻底的管理，包括定期检查.
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注1:From fiscal 2019, 医疗业务业绩在从HPP公司独立出来并将总部业绩重新分类为其他后，已单独整理.
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注2:根据从2022年10月开始实施的UIEP和HPP公司某些业务控制权的变化, 两家公司在2022财年的数据被整理得好像控制权的变化是从2022财年开始就开始的.
基于PRTR法的汇总结果(在需要评估的商业场所处理的处理量为1吨或更多的物质的汇总结果).
| 物质 | 政府. ordinance notification no. | 处理体积 | Emission volume | Transfer volume | Detoxification | |||||
|---|---|---|---|---|---|---|---|---|---|---|
| 大气 | Public water areas | 内部土壤 | In-ho使用 landfill | 污水处理系统 | Transfer in waste 处理 | Transfer in waste recycling | ||||
| Ethyl acrylate | [3] | 30 | - | - | - | - | - | - | 3.0 | 27 |
| n-Butyl acrylate | [7] | 195 | 1.6 | - | - | - | - | 1.2 | 0.0020 | 193 |
| 丙烯腈 | [9] | 526 | 3.2 | - | - | - | - | - | 0.0060 | 523 |
| 乙醛 | [12] | 203 | 0.18 | - | - | - | - | - | - | 203 |
| 乙腈 | [13] | 62 | 4.9 | - | - | - | - | - | 57 | - |
| 2,2’-Azobisisobutyronitrile | [16] | 6.1 | - | - | - | - | - | - | - | 6.1 |
| Antimony and its compounds | [31] | 9.1 | - | - | - | - | - | - | 0.91 | - |
| Isobutyraldehyde | [35] | 50 | 1.4 | - | - | - | - | - | - | 49 |
| 2-Ethylhexanoic acid | [51] | 5,799 | - | - | - | - | - | - | 5.9 | 5,786 |
| 埃塞尔苯 | [53] | 1.5 | 1.5 | - | - | - | - | - | - | - |
| Ethylenediamine | [59] | 1.6 | 0.15 | - | - | - | - | - | - | 1.4 |
| ε己内酰胺 | [76] | 42 | - | 0.014 | - | - | - | - | - | 42 |
| 二甲苯 | [80] | 1.5 | 1.5 | - | - | - | - | - | 0.016 | - |
| Chromium and trivalent chromium compound | [87] | 4.3 | - | - | - | - | - | 0.028 | 0.0066 | - |
| 氯乙烯 | (特别94) | 116,160 | 3.8 | 0.10 | - | - | - | - | - | 116,156 |
| 氯仿 | [127] | 5.3 | 0.28 | - | - | - | - | - | 3.1 | 0.53 |
| Cobalt and its compounds | [132] | 3.5 | - | 0.12 | - | - | - | - | - | 3.4 |
| 醋酸乙烯酯 | [134] | 52 | 5.4 | - | - | - | - | 3.7 | - | 43 |
| "Inorganic cyanide compounds (not including complex salts and cyanate)" | [144] | 15 | - | - | - | - | - | - | - | 15 |
| Cyclohexylamine | [154] | 6.4 | 0.36 | - | - | - | - | - | - | 6.1 |
| Methylene chloride | [186] | 320 | 4.2 | - | - | - | - | - | - | 316 |
| 二乙烯基苯 | [202] | 1.7 | - | - | - | - | - | - | - | 1.7 |
| 2,6-di-t-butyl-4-cresol | [207] | 49 | - | - | - | - | - | - | - | 49 |
| N,N-dimethylformamide | [232] | 1.7 | - | - | - | - | - | - | 1.7 | - |
| Organic tin compounds | [239] | 128 | - | 0.0000 | - | - | - | 0.067 | 0.51 | 2.8 |
| 苯乙烯 | [240] | 1,286 | 28 | - | - | - | - | - | 0.012 | 516 |
| n-dodecyl alcohol | [273] | 16 | - | - | - | - | - | - | - | 16 |
| Tolylene Diisocyanate | [298] | 6.5 | - | - | - | - | - | - | - | - |
| 甲苯 | [300] | 711 | 34 | - | - | - | - | 55 | 228 | 274 |
| 铅化合物 | (特别305) | 487 | - | 0.0002 | - | - | 0.0000 | 0.38 | 16 | 6.1 |
| Nickel compound | (特别309) | 1.0 | - | - | - | - | - | 0.32 | - | - |
| Bis-(2-ethylhexyl) phthalate | [355] | 8.4 | - | - | - | - | - | - | 2.2 | 4.0 |
| 正己烷 | [392] | 240 | 7.9 | - | - | - | - | 29 | 203 | - |
| Boron and its compounds | [405] | 24 | - | - | - | - | - | - | - | - |
| "Poly (oxyethylene) = alkyl = ether (C = 12-15 and other blends)" | [407] | 3.6 | - | - | - | - | - | - | - | - |
| Manganese and its compounds | [412] | 4.9 | - | - | - | - | - | - | 4.9 | - |
| 异丁烯酸甲酯 | [415] | 289 | 1.6 | - | - | - | - | - | 0.0070 | 288 |
| Methyl methacrylate | [420] | 173 | 0.90 | - | - | - | - | - | - | 172 |
| Methylnaphthalene | [438] | 1.3 | 0.006 | - | - | - | - | - | - | 1.2 |
| Methylenebis (4,1-phenylene) = diisocyanate | [448] | 1,534 | - | - | - | - | - | - | 0.010 | 1,531 |
| 128,458 | 101 | 0.24 | - | - | 0.0000 | 89 | 527 | 126,229 | ||
| 指数 | Calculation Method |
|---|---|
| Amount of Chemical 物质s Handled | Amount of substances subject to regulation by the PRTR Law handled [Scope: Production sites and research facilities in Japan] |
| Amount of Emissions / Transfer of Chemical 物质s | 受PRTR法管制的化学物质的排放量/转移量:排放量=进入空气的排放量+进入公共水域的排放量+进入现场土壤的排放量+现场填埋处理的排放量 转移量=转移到下水道的量+作为废物转移的量[范围:日本的生产基地和研究设施] |
| Amount of Chemical 物质s Subject to Detoxication | 《十大赌博娱乐平台》规定的需要解毒的化学物质的数量:解毒的数量=反应消耗的数量+燃烧消耗的数量, 等. [Scope: Production sites and research facilities in Japan] |
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- 11-96
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Amount of Chemical 物质 Emission and Transfer (PRTR Law) / Japan
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注意:由于总范围的变化，过去的数字已进行了追溯性修订.
指数 Calculation Method Amount of Emissions / Transfer of Chemical 物质s 受PRTR法管制的化学物质的排放量/转移量:排放量=进入空气的排放量+进入公共水域的排放量+进入现场土壤的排放量+现场填埋处理的排放量
排污量=排污量+排污量
Scope: Covers production sites and research facilities in Japan -
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Discharge of Volatile Organic Compounds (VOCs) into the Atmosphere / Japan
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注意:由于总范围的变化，过去的数字已进行了追溯性修订.
指数 Calculation Method VOC的排放 受PRTR法和日本化学工业协会监管的物质中挥发性有机化合物(VOC)排放到大气中的量 -
- 11-99
- 11-100
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氮氧化物的排放 / Japan
指数 Calculation Method 氮氧化物的排放 NOx排放量=Σ(每年废气风量× NOx浓度× 46 / 22).4) -
袜排放 / Japan
指数 Calculation Method 袜排放 SOx emissions =Σ(amount of SOx per year x 64 / 22.4)
- 11-103
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Soot and Dust Emissions / Japan
指数 Calculation Method Soot and Dust Emissions 烟尘排放量=Σ(每年废气风量×烟尘浓度)